Subscriber access provided by Mississippi State University Libraries
Article
Rapid Detection of Gaseous Compounds by Needle Trap Sampling and Direct Thermal-Desorption Photoionization Mass Spectrometry: Concept and Demonstrative Application to Breath Gas Analysis Juliane Kleeblatt, Jochen Klaus Schubert, and Ralf Zimmermann Anal. Chem., Just Accepted Manuscript • DOI: 10.1021/ac5039829 • Publication Date (Web): 17 Dec 2014 Downloaded from http://pubs.acs.org on December 20, 2014
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
Analytical Chemistry is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
1
Rapid Detection of Gaseous Compounds by Needle
2
Trap Sampling and Direct Thermal-Desorption
3
Photoionization Mass Spectrometry: Concept and
4
Demonstrative Application to Breath Gas Analysis
5
Juliane Kleeblatt,† Jochen Klaus Schubert ‡ and Ralf Zimmermann †*
6
†
7
University of Rostock, Dr.-Lorenz-Weg 1, 18059 Rostock, Germany and Comprehensive
8
molecular analytics, Helmholtz Zentrum München, Ingolstädter Landstraße 1, 85764
9
Neuherberg, Germany, ‡ Department of Anesthesia and Intensive Care, University of Rostock,
10
Joint Mass Spectrometry Center, Chair of Analytical Chemistry, Institute of Chemistry,
Schillingallee 35, 18057 Rostock, Germany
11 12
* Corresponding Author
13
E-mail:
[email protected],
[email protected]. Phone:
14
+49 (0) 381 498 6460. Fax: +49 (0) 381 498 118 6527.
15 16 17
ACS Paragon Plus Environment
1
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 2 of 28
18
KEYWORDS
19
Needle-trap micro-extraction, gas chromatography, single photon ionization, resonance enhanced
20
multiphoton ionization, time-of-flight mass spectrometry, alveolar sampling, propofol
21 22
ABSTRACT
23
A fast detection method to analyze gaseous organic compounds in complex gas mixtures was
24
developed, using a needle trap device (NTD) in conjunction with thermal-desorption
25
photoionization time-of-flight mass spectrometry (TD-PI-TOFMS). The mass spectrometer was
26
coupled via a deactivated fused silica capillary to an injector of a gas chromatograph. In the hot
27
injector the analytes collected on the NTD were thermally desorbed and directly transferred to
28
the PI-TOFMS ion source. The molecules are softly ionized either by single photon ionization
29
(SPI, 118 nm) or by resonance enhanced multiphoton ionization (REMPI, 266 nm) and the
30
molecular ion signals are detected in the TOF mass analyzer. Analyte desorption and subsequent
31
PI-TOFMS detection step only lasts ten seconds. The specific selectivity of REMPI (i.e. aromatic
32
compounds) and universal ionization characteristics render PI-MS as a promising detection
33
system. As a first, demonstrative application alveolar-phase breath gas of healthy, non-smoking
34
subjects was sampled on NTDs. While smaller organic compounds as acetone, acetaldehyde,
35
isoprene or cysteamine can be detected in the breath gas with SPI, REMPI depicts the aromatic
36
substances phenol and indole at 266 nm. In breath gas of a healthy, smoking male subject,
37
several xenobiotic substances such as benzene, toluene, styrene and ethylbenzene can be found
38
as well. Furthermore, the NTD-REMPI-TOFMS setup was tested for breath gas taken from a
ACS Paragon Plus Environment
2
Page 3 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
39
mechanically ventilated pig under continuous intravenous propofol (2,6-diisopropylphenol,
40
narcotic drug) infusion.
41 42
INTRODUCTION
43
Photoionization mass spectrometry (PI-MS) has been successfully used for on-line determination
44
of substances in complex gaseous mixtures.1-3 However, if direct on-line sampling is not possible
45
due to practical or legal constraints, analytes may be pre-concentrated onto adsorptive trapping
46
devices, such as solid phase microextraction (SPME), and subsequently subjected to the analysis
47
e.g. by GC/MS. Pawliszyn et al. developed the SPME method as an improved version of the
48
solid phase extraction (SPE) technique. A fused silica fiber coated with polymeric adsorbent (e.g.
49
polydimethylsiloxane or Carbowax/divinylbenzene) is exposed to the gaseous or liquid sampling
50
medium and subsequently thermal desorbed solvent-free e.g. in a gas chromatographic injector.4,
51
5
52
technique, which allows easier handling during sampling and desorption. The NTD is a stainless
53
steel needle packed with sorbent materials such as Carboxen, Carbopack, Tenax, divinylbenzene
54
or polydimethylsiloxane (PDMS).6-11 Depending on the application the adsorbent material and
55
arrangement (single- or multi-bed) can be adapted. The solvent-free method needs only small
56
sampling volume; however, it is also possible to enhance the sensitivity by increasing the
57
sampling volume. Therefore, the needle trap technique is restricted by breakthrough sampling
58
volume and not by equilibration time or dynamics such as SPME. Thus, the sampling can be
59
performed very fast. In this work the NTD sampling approach was combined with detection by
60
photoionization mass spectrometry.
Further developments by Pawliszyn et al. had led to the more robust needle trap device (NTD)
ACS Paragon Plus Environment
3
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 4 of 28
61
Photoionization comprises of single and multiphoton absorption/ionization processes (SPI and
62
MPI). A neutral molecule is ionizable by single photon ionization (SPI) if the energy of a single
63
vacuum-ultraviolet (VUV)-photon (λ < 200 nm) is equal to or higher than the ionization energy
64
of the substance. Thus, if the photon energy is high enough the ionization technique is applicable
65
to all organic substances. There are different possibilities to generate the required VUV-photons,
66
which include deuterium discharge lamps, F2-lasers (157 nm), synchrotron radiation, electron
67
beam pumped rare gas excimer lamps (EBEL) or frequency-tripled third harmonic generation of
68
Nd:YAG lasers.12-15
69
In contrast to the SPI process, MPI processes require much higher photon fluxes, achievable
70
solely by pulsed lasers. For analytical purposes, resonance enhanced multiphoton processes
71
(REMPI), where the photon energy is in resonance with an UV-spectroscopic state of the analyte
72
molecules, is the most common method used. In case of a one-color, two-photon resonance
73
enhanced multiphoton ionization process ((1+1)-REMPI, analytically most important REMPI
74
process) a resonance absorption of a UV photon (i.e. gas phase UV spectroscopic step) is
75
followed by the absorption of a second UV-photon of same laser pulse. If the sum of energies of
76
both absorbed photons equals or exceeds the ionization threshold of the substance, the substance
77
can be ionized with a rather high probability.16-18 REMPI and SPI mass spectrometry is known as
78
a sensitive and selective analytical technique for fast on-line analysis of molecules in complex
79
gaseous mixtures.
80
Breath gas analysis stands out as an ideal, non-invasive diagnosis method. Although the breath
81
gas is rather complex at the trace level, the matrix is comparably easy. Therefore, a complex,
82
time and cost consuming sample preparation step is not necessary. Due to the direct correlation
83
between substance concentration in blood and breath, analysis of breath gas may reduce the
ACS Paragon Plus Environment
4
Page 5 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
84
amount of invasive blood sampling steps. As the analysis of volatile organic compounds (VOCs)
85
in breath is suspected to understand biochemical processes in the body, to allow the
86
determination of disease types in clinical diagnosis, and to support the search for biomarkers, the
87
research field is continuously increasing. Different on-line and off-line analytical methods have
88
been developed.19-26 Due to the low concentrations of VOCs in breath, the already mentioned
89
pre-concentration methods were utilized and commonly combined with gas chromatography
90
mass spectrometry (GC-MS).27, 28 Due to the current trend to develop and apply soft ionization
91
mass spectrometers for on-line breath gas analysis, several techniques are based on chemical
92
ionization (CI).29 Examples include proton transfer reaction (time-of-flight) mass spectrometry
93
(PTR-MS or PTR-TOFMS), selected ion flow tube mass spectrometry (SIFT-MS), ion mobility
94
spectrometry (IMS) or extractive electrospray ionization mass spectrometry (EESI-MS).30-35
95
However, rather new PI-MS methods have been rarely applied in the field of breath analysis until
96
now. With SPI-TOFMS, compounds such as acetaldehyde, acetone, isoprene and phenol were
97
on-line detected in breath gas of non-smokers. In smokers breath a large number of xenobiotic
98
compounds are detectable. REMPI-TOFMS was applied for on-line measurements of aromatic
99
substances in the mouth space of smokers and for detection of breath nitric oxide.36-38
100
This publication reports on a new, fast coupling of needle trap devices (NTDs) and direct
101
thermal-desorption photoionization time-of-flight mass spectrometry for the analysis of gas
102
phase. The combination of trapping low concentrated volatile organic compounds, the sensitivity
103
and selectivity of photoionization process as well as the fast measurement within ten seconds,
104
qualifies the approach for rapid gas analysis. The experimental concept and setup is presented
105
and the applicability to breath gas analysis is shown by first case study results. NTD-TD-PI-
106
TOFMS was used for determination of substances in breath gas of healthy subjects (non-
ACS Paragon Plus Environment
5
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 6 of 28
107
smoking and smoking) as well as in mechanically ventilated animal model. As an option, a gas
108
chromatographic step was implemented for precise identification of measured compounds. The
109
use of photoionization mass spectrometry as a detector method for GC is reported in literature as
110
three-dimensional method (parameters: retention time, wavelength used for PI, molecular ion
111
mass).39-44
112 113
EXPERIMENTAL SECTION
114
Needle Trap Devices. The used triple-bed NTDs were produced by Shinwa Ltd., Japan and were
115
purchased from PAS Technology, Germany. The 22 gauge needles are 7 cm long with conical tip
116
(figure 2) and filled with respectively 1 cm of polydimethylsiloxane (PDMS, 100/120 mesh),
117
Carbopack B (60/80 mesh) and Carboxen 1000 (60/80 mesh). The very small grain sizes of the
118
adsorbent materials were chosen to ensure the interaction of the analytes with the adsorbents and
119
therefore, to prevent the channeling effect.45 Before using the NTDs, a conditioning step is
120
essential to eliminate contaminations from production process. Therefore, the needles (20 pieces
121
simultaneously) are flushed by a continuous helium flow and heated in a home-made solid
122
aluminum block means ceramic heating plate (C-MAG HS7 IKAMAG, IKA) controlled by
123
contact thermometer (ETS-D5). The conditioning temperature was 290 °C for 12 hours. Before
124
every usage, the needles are conditioned for 30 min at 290 °C again. For storage and in-between
125
usage each NTD is sealed with two Teflon caps.
126
Instrumentation.
127
a) Needle trap device thermal-desorption photoionization mass spectrometer (NTD-TD-PI-MS)
ACS Paragon Plus Environment
6
Page 7 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
128
The injector of an Agilent/HP 5890 gas chromatograph was used for thermal desorption of
129
needle trap devices. The direct coupling to a photoionization time-of-flight mass spectrometer
130
ensures a rapid measurement of the desorbed substances (figure 1). Within less than ten seconds,
131
the sampled compounds are desorbed from the NTD at 290 °C in the injector, using SPME-GC
132
inlet liner (Supelco, 78.5 mm × 6.5 mm × 0.75 mm) and being directly transferred in helium flow
133
(Split: 1:2.5) via a deactivated heated fused silica capillary (BGB Analytik AG, 250 µm ID,
134
350 µm OD, length 2.8 m, temperature 250 °C) to the ion source of the time-of-flight mass
135
spectrometry. The used laser mass spectrometer (REMPI/SPI-TOFMS) was already described in
136
detail.46, 47 Briefly, for REMPI the optical parametric oszillator (OPO) system (GWU-
137
Lasertechnik GmbH, Erftstadt, Germany) is pumped by the third harmonic of a Nd:YAG
138
laser (Continuum Surelite III, Santa Clara, USA, repetition rate 10 Hz) to generate UV laser
139
pulses. The wavelength is tunable between 218 and 345 nm. For SPI, the third harmonic
140
frequency (355 nm) of the same laser is used for direct third harmonic generation (THG) of
141
118 nm pulses (photon energy: 10.49 eV) in a xenon filled gas cell. The laser beam with a
142
wavelength of either 266 nm (REMPI) or 118 nm (SPI) was directly focused underneath the
143
effusive molecular beam gas inlet. The generated ions were captured by electrostatic acceleration
144
fields in the ion source of a reflectron time-of-flight mass spectrometer (Kaesdorf, Munich,
145
Germany) and subsequently detected by a multichannel plate (MCP) detector. Data analysis was
146
performed by home written LabView software tools.
ACS Paragon Plus Environment
7
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 8 of 28
147 148
Figure 1. Measurement setup: needle trap thermal desorption in a hot gas chromatographic inlet
149
coupled with photoionization (SPI/REMPI) time-of-flight mass spectrometer; direct and rapid
150
measurement leads to simultaneous detection of substances in at most 10 seconds; variation with
151
GC column provides detection after substance-specific retention time.
152
b) Needle trap device thermal-desorption gas chromatography photoionization mass
153
spectrometry (NTD-TD-GC-PI-MS)
154
Optional it is possible to include a gas chromatographic step for identification of measured
155
substances. In spite of losing the speed of the direct transfer method, the selectivity of REMPI
156
and SPI-MS is enhanced by a further dimension. For this purpose, a DB-5MS capillary column
157
(250 µm ID; 0.25 µm film thickness; J&W Scientific/Agilent Technologies, Santa Clara,
158
California, USA) was used with different lengths and temperature programs for REMPI and SPI-
159
TOFMS measurements. In case of REMPI, a 10 m column with a short temperature program
160
(40 °C for 1 min, 12 °C/min to 250 °C for 1 min) was optimal. Due to the fact that also rather
161
volatile compounds are detectable with SPI-TOFMS, the measurements were performed with a
162
30 m long column and a modified temperature program (30 °C for 1 min, 10 °C/min to 250 °C
ACS Paragon Plus Environment
8
Page 9 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
163
for 1 min). An average of 5 mass spectra was used for GC measurements, thus, two data points
164
per second were detected.
165
Demonstration measurements: In Vivo Breath Gas Sampling. The healthy, smoking and non-
166
smoking volunteering subjects were wearing a nose clip and breathe into a u-shaped device,
167
which included a port for needle trap device and a connection to capnometer (Capnogard EtCO2
168
Monitor, Novametrix Medical Systems INC.). Hence, the sampling was CO2-controlled, so that
169
only the alveolar breath was pre-concentrated on NTD (see supporting information file available
170
free of charge via the internet, figure S-1). The adsorption was managed by coupling a 1 ml
171
single use syringe onto the Luer connection of the needle traps. Subsequently, the breath of the
172
alveolar phase was pulled through the needle and pushed back again by agitating the syringe.
173
The process was repeated for 30 times, hence, the sampling volume was 30 ml. Depending on
174
the respiratory frequency of the subject, the sampling time was between 2 to 3 minutes. The
175
average flow rate was approximately 25 to 30 ml/min.
176
The volunteer smoker breathed into the device for two NTD samples, directly after smoking a
177
cigarette. After one hour without smoking, again two breath samples were taken. All subjects did
178
not eat nor brush their teeth for more than 1 hour before sampling.
179
For the healthy volunteer group, two female (21 and 30 years old) and two male (23 and 29 years
180
old) subjects were measured. The 49 years old male smoker indicated that he has been smoking
181
for about 30 years and by now he smokes 30 to 40 cigarettes (1½-2 packs) per day.
182
For determining propofol in breath gas, a pig of 25.6 kilos was mechanically ventilated
183
undergoing surgery (supporting information figure S-2 b). The anesthesia was inducted with
184
100 mg propofol (1%), 0.15 mg Fentanyl and 20 mg Nimbex. The intravenous infusion of
ACS Paragon Plus Environment
9
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 10 of 28
185
propofol (2%) was maintained with a flow of 5 ml/h for about 8 hours. The alveolar sampling
186
was realized connecting a t-piece into expiration tube and adsorbing respectively 20 ml of breath
187
gas on four needle trap devices over a period of one hour. Additionally, an inspiration sample
188
was taken from breathing hose.
189 190
RESULTS AND DISCUSSION
191
Evaluation of the developed NTD-TD-PI-MS coupling. After inserting the loaded needle trap
192
device into the hot GC inlet, thermal desorption takes place and desorbed molecules are directly
193
transferred into mass spectrometer within seconds. The desorption process itself lasts only a
194
fraction of a second and thus a rather fast measurement is required in order to capture the
195
dynamical behavior of the desorption process. The laser system operates with a repetition rate of
196
10 Hz, thus, 10 mass spectra can be recorded per second. A sufficiently precise molecular signal
197
vs. time curve of the desorption process could be recorded (supporting information figure S-
198
2 a,b). The peak areas of these curves were used for quantification. The optimization before first
199
measurements included the trial of split mode and according helium flow as well as selection of
200
GC head pressure and temperatures of whole system. Best results were found for an injection
201
split of 1:2.5, a head pressure of 50 kPa, an inlet temperature of 290 °C for PDMS/Carbopack
202
B/Carboxen1000 packed needle trap device and a temperature of 250 °C for transfer capillary
203
and ion source.
204
The evaluation of the new coupled method was realized by using a gas standard mixture
205
containing benzene (0.99 ppm), toluene (0.93 ppm) and 1,2,4-trimethylbenzene (1.3 ppm). The
206
standard gas was diluted means evacuated 20 ml headspace vials so that every compound was in
ACS Paragon Plus Environment
10
Page 11 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
207
a concentration of approximately 100, 200, 300, 400 and 500 ppb. The differences in starting
208
concentrations were recognized in acquisition (supporting information figure S-2 e,f). In each
209
case 10 ml of the diluted standard were adsorbed on a needle trap device and desorbed in the GC
210
inlet directly coupled to mass spectrometer. Each concentration was prepared and pre-
211
concentrated four times and the limits of detection (LOD) and limits of quantitation (LOQ) were
212
determined in accordance with DIN 32645 (table 1). Note that the signals and therefore, the
213
limits of detection increase linear with rising sampling volume until the breakthrough volume of
214
the respective substance is reached.
215
Table 1. Limits of detection (LOD) and limits of quantitation (LOQ) of benzene, toluene and
216
1,2,4-trimethylbenzene determined with REMPI and SPI using a sampling volume of 10 ml.
Compound
LOD REMPI
LOQ REMPI
LOD SPI
LOQ SPI
(ppb)
(µg)
(ppb)
(µg)
(ppb)
(µg)
(ppb)
(µg)
Benzene
14.1
49.1
60.4
210.5
30.3
105.6
124.0
432.1
Toluene
10.3
42.3
44.3
182.1
27.0
111.0
110.9
455.9
1,2,4-TMB
11.0
59.0
48.2
258.5
27.4
146.9
116.2
623.1
217 218
The results of standard gas mixture measurements show that the coupling is functioning
219
reproducible and in a low concentration range. 10 ml of the diluted standard gas mixture are
220
sufficient to obtain LOD in the lower ppb range for all substances and ionization methods.
221
Performing a second desorption of the already desorbed needle trap showed that no carryovers
222
were generated.
223
More detailed information is given in supporting information file.
ACS Paragon Plus Environment
11
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 12 of 28
224 225
Application Demonstration: Use of NTD-TD-PI-MS for fast breath gas analysis.
226
a) Analysis of breath gas of healthy, non-smoking subjects
227
The needle trap device thermal-desorption photoionization mass spectrometric method was
228
applied to analyze the breath gas of healthy non-smoking subjects. According to their specific
229
selectivity and sensitivity profile, the different photoionization methods REMPI and SPI address
230
different breath gas analytes. Whereas SPI depicts more volatile substances such as acetone,
231
acetaldehyde, isoprene and cysteamine, it is possible to detect the traces of aromatic breath gas
232
compounds such as phenol and indole by REMPI. The named substances were confirmed by
233
additional use of the gas chromatographic separation step (see below). Both techniques show
234
background substances from needle trap adsorption material (figure 2). Thus, all mass spectra
235
were corrected by blank mass spectra subtraction. Note that the spectra are corrected due to the
236
variation of laser intensity for every measurement. Therefore, REMPI energy was measured
237
behind ion source and the laser power was logged for SPI measurements.
ACS Paragon Plus Environment
12
Page 13 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
238 239
Figure 2. Mass spectra of breath gas of healthy, non-smoking subjects (2 female, 2 male) each
240
measured by REMPI (266 nm) and SPI (118 nm). Left: REMPI measurements of respectively
241
three averaged breath gas samples which are corrected by room air/needle trap background mass
242
spectrum above; right: SPI measurements of respectively three averaged breath gas samples
243
which are corrected by room air/needle trap background mass spectrum above.
244
The averaged REMPI mass spectra of four healthy, non-smoking subjects (respectively three
245
samples) are shown on the left in figure 2. Phenol and indole are detected in the breath gas of all
246
subjects. Both substances have been described previously in literature as breath gas compounds,
247
using time-intensive conventional enrichment and chemical analysis technologies. Indole
248
(m/z 117) derives from catabolism of the amino acid tryptophan and decreases significantly in
ACS Paragon Plus Environment
13
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 14 of 28
249
breath gas of patients with liver diseases because of higher levels of free tryptophan.48-50
250
Additionally, it was found in connection with halitosis (bad breath), because of production from
251
bacteria in mouth.51 The detected phenol (m/z 94) can arise endogenous from metabolism of
252
aromatic amino acids. Statheropolous et al. described the determination of phenol in the breath
253
gas of fasting subjects.52 Phenol, however, is contained in many foodstuffs (e.g. fruits, coffee)
254
and thus, may also partly be of exogenous nature. The relation between signal intensities of both
255
substances shows a variation depending on measured subject. All breath gas samples show in
256
addition a yet unidentified molecular signal at m/z 212. Due to the fact that this signal is only
257
measurable by REMPI, the m/z 212 compound is of aromatic nature. Additionally, only for 21
258
years old female a rather intense aromatic peak at m/z 148 was detected.
259
The averaged SPI mass spectra are shown on the right side of figure 2. The detected acetone
260
(m/z 58) is of endogenous origin since it was already described as decarboxylation product of
261
acetoacetate, which is a result of dextrose metabolism and lipolysis, and acetyl-CoA.21 Acetone
262
has been frequently detected in breath gas in a concentration range of more than 100 ppb up to a
263
few thousand part-per-billion and often a relation between higher acetone concentration (up to
264
ppm level) and diabetes was experienced.53-56 Furthermore, the endogenous substance
265
acetaldehyde (m/z 44) is measurable in breath gas using single photon ionization. The compound
266
derives from ethanol metabolism in liver and was found in the ppb concentration range in breath
267
gas of healthy persons.57 The endogenous origin of isoprene is not entirely clear, but it was
268
already described as a by-product of cholesterol biosynthesis and found in breath gas in a
269
concentration range between a few ppb to a few hundred ppb.56, 58, 59 The compound with m/z 77
270
was assigned to cysteamine. This assignation was confirmed by the GC analysis (NTD-TD-GC-
271
SPI-MS, figure 4 a) with a standard. Cysteamine is the decarboxylation product of the amino
ACS Paragon Plus Environment
14
Page 15 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
272
acid cysteine and plays a decisive role in the cysteine metabolic cycle as product of synthesis and
273
degradation of coenzyme A. Furthermore, the oxidation of cysteamine is indispensable for the
274
production of hypotaurine and finally of taurine and that cysteamine is a major product of
275
metabolism of pantheinase.60, 61 Free, endogenous cysteamine was already found in tissues, e.g.
276
of kidney and liver.62, 63 Due to the fact that cysteamine is difficult to detect in EI-MS (strong
277
fragmentation to m/z 30, after bond cleavage of C-C bond, NIST Chemistry WebBook) its
278
occurrence in breath gas is not well covered in the literature. On-line mass spectrometry with soft
279
ionization techniques, such as the here used SPI, is preferred to detect cysteamine in breath gas.
280
The assignation of m/z 77 to cysteamine, however, is supported by data from Martínez-Lozano et
281
al., who were able to detect the substance in breath gas using electrospray ionization and tandem
282
mass spectrometry.64
283
b) Analysis of breath gas of a healthy, smoking subject
284
The breath gas of the smoking person (figure 3) shows same substances as in breath from healthy
285
non-smokers (figure 2) and additional smoking related compounds. Most of the substances are of
286
exogenous origin, which can be clearly seen by comparing mass spectra obtained from sampling
287
directly after smoking with results obtained from samples one hour after smoking a cigarette. All
288
smoking related compounds result in lower signals or complete absence (below LOD) after one
289
hour. Same experiences were gained in literature mainly in terms of benzene, toluene, styrene,
290
ethylbenzene and xylenes.65-68 Poli et al. determined the breath of non-smokers, smokers and
291
subjects with lung diseases as lung cancer and described significantly higher concentrations of
292
ethylbenzene, xylenes, trimethylbenzene, toluene and benzene in breath gas of smoker compared
293
with non-smoker. Using 13 selected substances a discrimination of the groups (non-smoker,
294
smoker, NSCL, COPD) is possible.69 As marker for smoking 2,5-dimethylfuran (m/z 96) is
ACS Paragon Plus Environment
15
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 16 of 28
295
frequently described because of total absence in breath gas of healthy, non-smoking subjects.24,
296
68, 70, 71
297
substances not occurring in breath of non-smoker.
But also furan (m/z 68) and methyl furan (m/z 82) are known as smoking related
298 299
Figure 3. Mass spectra of breath gas of healthy, smoking subject (49 years, 20-40 cigarettes per
300
day) measured by REMPI (266 nm) and SPI (118 nm). Left: REMPI measurements of breath gas
301
samples (corrected by room air/needle trap background mass spectrum above) as well as
302
logarithmic scales for better presentation of small peaks; right: SPI measurements of breath gas
303
samples (corrected by room air/needle trap background mass spectrum above) as well as
304
logarithmic scales for better presentation of small peaks.
ACS Paragon Plus Environment
16
Page 17 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
305
In figure 3 the differences between SPI (118 nm) and REMPI at a wavelength of 266 nm are
306
shown. While benzene (m/z 78) and toluene (m/z 92) are measurable by both techniques,
307
substances as styrene (m/z 104), ethylbenzene (m/z 106), 1,2,4-trimethylbenzene (m/z 120), m-,
308
p- and o-xylene (m/z 106) only were detected using REMPI. The NTD-TD-SPI-MS
309
measurement also shows signals at m/z 82 and m/z 96, which can be assigned to methylated and
310
dimethylated furan.36 The corresponding GC experiment (see below) indicates several isomers
311
for these masses. Directly after smoking, a great number of peaks result for both ionization
312
methods, but many exogenous compounds in the breath gas disappear during the hour without
313
smoking. With REMPI 266 nm (figure 3, left side) several peaks in the mass range from m/z 130
314
to m/z 200 appear directly after smoking. After only 1 hour almost all peaks had disappeared. A
315
similar pattern can be seen for SPI 118 nm (figure 3, right side). Especially, peaks with a mass-
316
to-charge ratio between 80 and 120 decrease in their intensity.
317
Confirmation of compound assignation: Including gas chromatographic separation. For
318
confirmation of the assignation of the detectable breath gas compounds, a gas chromatographic
319
step was implemented to use the three-dimensionality of the method (retention time, wavelength,
320
mass of molecular ion). Therefore, 10 µl of headspace above the appropriate pure substance were
321
put into an evacuated 20 ml headspace vial and afterwards the pressure was compensated by
322
helium. A sampling volume of 1 ml was adsorbed on needle trap device and subsequently
323
measured by presented NTD-GC-PI-TOFMS. The described procedure was repeated for every
324
substance with exception of acetaldehyde and acetone (1 µl headspace sufficient) as well as
325
cysteamine (10 ml headspace directly adsorbed on NTD). The several gas chromatograms of
326
relevant mass traces were merged to one complete chromatogram.
ACS Paragon Plus Environment
17
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 18 of 28
327 328
Figure 4. NTD-TD-GC-TOFMS: Comparison of results for gas chromatographic measurements
329
of NTD smoker and non-smoker breath gas samples measured by a) SPI-TOFMS and b) REMPI-
330
TOFMS. Below: results for separately detected pure substances (combined chromatograms).
331
In figure 4 b) the comparison between the breath gas samples of non-smoker and smoker directly
332
and 1 hour after smoking measured with REMPI (266 nm) including gas chromatographic
333
separation is presented. Additionally, the determined gas chromatograms of the pure substances
334
are shown to demonstrate the successful identification. As discussed in last section the
335
exogenous smoking related compounds (benzene, toluene, ethylbenzene, styrene, xylenes)
336
decrease during 1 hour without smoking. Hence, the chromatograms nearly match the non-
337
smoking ones. Under the used GC conditions m- and p-xylene as well as o-xylene and styrene
ACS Paragon Plus Environment
18
Page 19 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
338
were not separated. The unknown substance at m/z 212 turns out to be at least five, potentially
339
isomeric compounds.
340
Showing the soft ionization, the mass spectra of detected compounds at the appropriate retention
341
time (room air, breath gas and pure substance) are presented in the supporting information (non-
342
smoker: S-3 to S-6 and smoker: S-7 to S-16).
343
In figure 4 a) the SPI chromatograms of breath gas of non-smoker and smoker (directly and 1
344
hour after smoking) as well as pure substances (below) are shown. As already seen in REMPI
345
measurements the smoking related compounds decrease; thus, the chromatograms assimilate to
346
non-smoking result. Despite the longer GC column and slower temperature program toluene and
347
cysteamine are eluting nearly at same retention time. Because of the strong tailing of acetone it is
348
not completely separated from acetaldehyde peak. The already mentioned m/z 77 appears at the
349
same retention time as the pure substance cysteamine. For m/z 82 three peaks result in
350
chromatogram, thus, probably those are the two possible methylfuran isomers and a further
351
unknown compound. Likewise, three peaks appear for m/z 96, which are possibly the isomers of
352
dimethylfuran (including 2,5-dimethylfuran) and ethylfuran. The substance at m/z 80 is also yet
353
unidentified.
354
A comparison between appearing substances in breath gas of non-smoker and smoker directly
355
after smoking is shown in table S-1 (supporting information) in terms of signal-to-noise ratios.
356
Substances occurring both in breath of non-smoking and smoking subject have mostly higher
357
signals in smoker’s odor. The table also shows the used photoionization method (SPI 118 nm or
358
REMPI 266 nm) at which the respective substance was detectable. In addition, the SPI mass
ACS Paragon Plus Environment
19
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 20 of 28
359
spectra at appropriate retention time are shown in supporting information file (non-smoker: S-17
360
to S-20 and smoker: S-21 to S-26).
361
Application of NTD-TD-PI-MS: Analysis of breath gas from mechanically ventilated
362
animal model. A further application of NTD-REMPI-TOFMS demonstrates that the narcotic
363
drug propofol can easily be detected in breath gas using a wavelength of 276.9 nm.72 The
364
detailed results are shown and discussed in the supporting information file.
365 366
CONCLUSIONS
367
In summary, a method and device for fast analysis of volatile compounds based on needle trap
368
device sampling and a direct in-injector thermal desorption photoionization time-of-flight mass
369
spectrometer was established and successful tested. A single measurement only takes some
370
seconds. With a special auto sampler device; thus, more than 100 measurements per hour would
371
be performable. Detection limits in the mid-lower ppb range were achieved with 10 ml gas
372
samples. For validation and compound identification purposes, a gas chromatographic step can
373
be optionally implemented.
374
The first demonstrative application on breath gas showed different substances detectable in the
375
single or multiphoton ionization mode. Using SPI, more volatile compounds as acetone,
376
acetaldehyde, isoprene and cysteamine are measurable in the current setup. REMPI (266 nm) is
377
especially suitable for aromatics; thus, it was possible to measure substances as phenol and
378
indole in breath gas. In case of healthy smoker, additionally exogenous substances such as
379
benzene, toluene, ethylbenzene, styrene, xylenes, 1,2,4-trimethylbenzene and benzaldehyde are
ACS Paragon Plus Environment
20
Page 21 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Analytical Chemistry
380
measurable. The breath gas measurements of medically ventilated pig undergoing surgery
381
demonstrate, that propofol is measurable in the breath gas of anaesthetized subjects using NTD-
382
TD-REMPI-TOFMS.
383
In comparison with vacuum ionization techniques (such as EI or PI, ionizing at 10-5 mbar) the
384
above mentioned CI-MS techniques such as PTR-MS or SIFT ionize at relatively high pressures
385
(10-3-10-1 mbar), which is beneficial for the achievable LOD: More ions can be produced in an
386
ionization process with given ionization agent concentrations and ionization cross sections in a
387
volume unit, if the pressure is higher and vice versa. The ionization pressure related LOD
388
advantage in CI-MS methods, however, is accompanied by an increased artifact-ion formation
389
(i.e. cluster- and adduct-ion formation or fragmentation). The use of the NTD sampling and
390
enrichment technology helps to compensate the inherent lower LOD of vacuum single photon
391
ionization (SPI). However, due to the reduced artifact formation and fragmentation as well as the
392
specific selectivity (REMPI), the application of PIMS has unique inherent advantages as well.
393
With SPI furthermore compounds, which are difficult detectable by CI based methods can be
394
addressed (e.g. alkanes).
395
Although we have not shown quantitative data for the breath gas demonstrative examples, the
396
method in principle can be used for quantitative analysis. In fact for real applications a sampling
397
system using a bleeding-in of an isotope labeled standard (e.g. 13C-toluene) would be used such
398
as for quantitation of on-line PIMS measurements.
399
In conclusion, the new coupled NTD-TD-SPI/REMPI-TOFMS method is promising and
400
suggests further development. The specific selectivity of the used ionization method allows
401
addressing volatile compounds which are not so easily detected by other on-line and off-line
ACS Paragon Plus Environment
21
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 22 of 28
402
methods. In the here chosen demonstrative application of breath gas analysis is, for example
403
cysteamine. Further research will concentrate on new application fields (e.g. combustion
404
effluents and process gases) and improving of limit of detection in the ppt concentration range by
405
using e.g. modern laser systems and optimized THG gas cells.
406 407
ACKNOWLEDGEMENT
408
The authors acknowledge Dr. Dennis Kleeblatt for synthesis and purification of propofol
409
metabolites as well as Janet Hofmann and Dr. Patricia Fuchs for assistance in sampling of breath
410
gas of animal model.
411
Funding Sources
412
This work was funded by the Interdisciplinary Faculty (INF) of the University of Rostock in
413
terms of a scholarship (J.K.).
414 415
SUPPORTING INFORMATION AVAILABLE
416
Additional information as noted in text. This material is available free of charge via the Internet
417
at http://pubs.acs.org.
418 419
REFERENCES
420
(1)
Adam, T. W.; Clairotte, M.; Streibel, T.; Elsasser, M.; Pommeres, A.; Manfredi, U.;
421
Carriero, M.; Martini, G.; Sklorz, M.; Krasenbrink, A.; Astorga, C.; Zimmermann, R.
422
Analytical and Bioanalytical Chemistry 2012, 404, 273-276.
ACS Paragon Plus Environment
22
Page 23 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
423
Analytical Chemistry
(2)
424 425
Mitschke, S.; Adam, T.; Streibel, T.; Baker, R. R.; Zimmermann, R. Analytical Chemistry 2005, 77, 2288-2296.
(3)
426
Qi, F.; Yang, R.; Yang, B.; Huang, C.; Wei, L.; Wang, J.; Sheng, L.; Zhang, Y. Review of Scientific Instruments 2006, 77.
427
(4)
Belardi, R. P.; Pawliszyn, J. B. Water pollution research journal of Canada 1989, 24.
428
(5)
Grote, C.; Pawliszyn, J. Analytical Chemistry 1997, 69, 587-596.
429
(6)
Wang, A.; Fang, F.; Pawliszyn, J. Journal of Chromatography A 2005, 1072, 127-135.
430
(7)
Eom, I. Y.; Tugulea, A. M.; Pawliszyn, J. Journal of Chromatography A 2008, 1196-
431 432
1197, 3-9. (8)
433 434
2009, 81, 5851-5857. (9)
435 436
Mieth, M.; Schubert, J. K.; Gröger, T.; Sabel, B.; Kischkel, S.; Fuchs, P.; Hein, D.; Zimmermann, R.; Miekisch, W. Analytical Chemistry 2010, 82, 2541-2551.
(10)
437 438
Mieth, M.; Kischkel, S.; Schubert, J. K.; Hein, D.; Miekisch, W. Analytical Chemistry
Trefz, P.; Kischkel, S.; Hein, D.; James, E. S.; Schubert, J. K.; Miekisch, W. Journal of Chromatography A 2012, 1219, 29-38.
(11)
439
Trefz, P.; Rösner, L.; Hein, D.; Schubert, J. K.; Miekisch, W. Analytical and Bioanalytical Chemistry 2013, 1-11.
440
(12)
Butcher, D. J. Microchemical Journal 1999, 62, 354-362.
441
(13)
Hanley, L.; Zimmermann, R. Analytical Chemistry 2009, 81, 4174-4182.
442
(14)
Mühlberger, F.; Wieser, J.; Ulrich, A.; Zimmermann, R. Analytical Chemistry 2002, 74,
443 444 445
3790-3801. (15)
Zimmermann, R.; Lenoir, D.; Kettrup, A.; Nagel, H.; Boesl, U. Symposium (International) on Combustion 1996, 26, 2859-2868.
ACS Paragon Plus Environment
23
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 24 of 28
446
(16)
Boesl, U. Journal of Physical Chemistry 1991, 95, 2949-2962.
447
(17)
Boesl, U.; Zimmermann, R.; Weickhardt, C.; Lenoir, D.; Schramm, K. W.; Kettrup, A.;
448 449
Schlag, E. W. Chemosphere 1994, 29, 1429-1440. (18)
450 451
Ledingham, K. W. D.; Singhal, R. P. International Journal of Mass Spectrometry and Ion Processes 1997, 163, 149-168.
(19)
452
Buszewski, B.; Kesy, M.; Ligor, T.; Amann, A. Biomedical Chromatography 2007, 21, 553-566.
453
(20)
Kim, K. H.; Jahan, S. A.; Kabir, E. TrAC - Trends in Analytical Chemistry 2012, 33, 1-8.
454
(21)
Miekisch, W.; Schubert, J. K.; Noeldge-Schomburg, G. F. E. Clinica Chimica Acta 2004,
455
347, 25-39.
456
(22)
Badjagbo, K. Clinical Chemistry and Laboratory Medicine 2012, 50, 1893-1902.
457
(23)
Cao, W.; Duan, Y. Critical Reviews in Analytical Chemistry 2007, 37, 3-13.
458
(24)
Ligor, M.; Ligor, T.; Bajtarevic, A.; Ager, C.; Pienz, M.; Klieber, M.; Denz, H.; Fiegl,
459
M.; Hilbe, W.; Weiss, W.; Lukas, P.; Jamnig, H.; Hackl, M.; Buszewski, B.; Miekisch,
460
W.; Schubert, J.; Amann, A. Clinical Chemistry and Laboratory Medicine 2009, 47, 550-
461
560.
462
(25)
463 464
129. (26)
465 466
Amann, A.; Španěl, P.; Smith, D. Mini-Reviews in Medicinal Chemistry 2007, 7, 115-
Di Francesco, F.; Fuoco, R.; Trivella, M. G.; Ceccarini, A. Microchemical Journal 2005, 79, 405-410.
(27)
Blount, B. C.; Kobelski, R. J.; McElprang, D. O.; Ashley, D. L.; Morrow, J. C.;
467
Chambers, D. M.; Cardinali, F. L. Journal of Chromatography B: Analytical
468
Technologies in the Biomedical and Life Sciences 2006, 832, 292-301.
ACS Paragon Plus Environment
24
Page 25 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
469
Analytical Chemistry
(28)
470 471
34, 2705-2711. (29)
472 473
(30)
Blake, R. S.; Whyte, C.; Hughes, C. O.; Ellis, A. M.; Monks, P. S. Analytical Chemistry 2004, 76, 3841-3845.
(31)
476 477
Amann, A.; Poupart, G.; Telser, S.; Ledochowski, M.; Schmid, A.; Mechtcheriakov, S. International Journal of Mass Spectrometry 2004, 239, 227-233.
474 475
Alonso, M.; Godayol, A.; Antico, E.; Sanchez, J. M. Journal of Separation Science 2011,
Schwoebel, H.; Schubert, R.; Sklorz, M.; Kischkel, S.; Zimmermann, R.; Schubert, J. K.; Miekisch, W. Analytical and Bioanalytical Chemistry 2011, 401, 2079-2091.
(32)
Trefz, P.; Schmidt, M.; Oertel, P.; Obermeier, J.; Brock, B.; Kamysek, S.; Dunkl, J.;
478
Zimmermann, R.; Schubert, J. K.; Miekisch, W. Analytical Chemistry 2013, 85, 10321-
479
10329.
480
(33)
Španěl, P.; Smith, D. Mass Spectrometry Reviews 2011, 30, 236-267.
481
(34)
Vautz, W.; Nolte, J.; Fobbe, R.; Baumbach, J. I. Journal of Breath Research 2009, 3.
482
(35)
Chen, H.; Wortmann, A.; Zhang, W.; Zenobi, R. Angewandte Chemie - International
483 484
Edition 2007, 46, 580-583. (36)
485 486
Mühlberger, F.; Streibel, T.; Wieser, J.; Ulrich, A.; Zimmermann, R. Analytical Chemistry 2005, 77, 7408-7414.
(37)
487
Zimmermann, R.; Dorfner, R.; Kettrup, A. Journal of Analytical and Applied Pyrolysis 1999, 49, 257-266.
488
(38)
Short, L. C.; Frey, R.; Benter, T. Applied Spectroscopy 2006, 60, 217-222.
489
(39)
Zimmermann, R.; Welthagen, W.; Gröger, T. Journal of Chromatography A 2008, 1184,
490
296-308.
ACS Paragon Plus Environment
25
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
491
(40)
492
Page 26 of 28
Gullett, B. K.; Oudejans, L.; Tabor, D.; Touati, A.; Ryan, S. Environmental Science and Technology 2012, 46, 923-928.
493
(41)
Matsui, T.; Uchimura, T.; Imasaka, T. Analytica Chimica Acta 2011, 694, 108-114.
494
(42)
Nakamura, N.; Uchimura, T.; Watanabe-Ezoe, Y.; Imasaka, T. Analytical Sciences 2011,
495 496
27, 617-622. (43)
497 498
Material Cycles and Waste Management 2008, 10, 24-31. (44)
499 500
Eschner, M. S.; Selmani, I.; Gröger, T. M.; Zimmermann, R. Analytical Chemistry 2011, 83, 6619-6627.
(45)
501 502
Zimmermann, R.; Mühlberger, F.; Fuhrer, K.; Gonin, M.; Welthagen, W. Journal of
Filipiak, W.; Filipiak, A.; Ager, C.; Wiesenhofer, H.; Amann, A. Journal of Breath Research 2012, 6.
(46)
503
Mühlberger, F.; Hafner, K.; Kaesdorf, S.; Ferge, T.; Zimmermann, R. Analytical Chemistry 2004, 76, 6753-6764.
504
(47)
Mühlberger, F. PhD Thesis, Technische Universität, München, 2003.
505
(48)
Turner, M. A.; Bandelow, S.; Edwards, L.; Patel, P.; Martin, H. J.; Wilson, I. D.;
506 507
Thomas, C. L. P. Journal of Breath Research 2013, 7. (49)
Van den Velde, S.; Nevens, F.; Van hee, P.; van Steenberghe, D.; Quirynen, M. Journal
508
of Chromatography B: Analytical Technologies in the Biomedical and Life Sciences
509
2008, 875, 344-348.
510
(50)
Ross, B. M. BMC Research Notes 2008, 1.
511
(51)
van den Velde, S.; Quirynen, M.; Van hee, P.; van Steenberghe, D. Journal of
512
Chromatography B: Analytical Technologies in the Biomedical and Life Sciences 2007,
513
853, 54-61.
ACS Paragon Plus Environment
26
Page 27 of 28
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
514
Analytical Chemistry
(52)
515
Statheropoulos, M.; Agapiou, A.; Georgiadou, A. Journal of Chromatography B: Analytical Technologies in the Biomedical and Life Sciences 2006, 832, 274-279.
516
(53)
Turner, C.; Španěl, P.; Smith, D. Physiological Measurement 2006, 27, 321-337.
517
(54)
Schwarz, K.; Filipiak, W.; Amann, A. Journal of Breath Research 2009, 3.
518
(55)
Ueta, I.; Saito, Y.; Hosoe, M.; Okamoto, M.; Ohkita, H.; Shirai, S.; Tamura, H.; Jinno, K.
519
Journal of Chromatography B: Analytical Technologies in the Biomedical and Life
520
Sciences 2009, 877, 2551-2556.
521
(56)
522 523
Chromatography B: Biomedical Sciences and Applications 1999, 729, 75-88. (57)
524 525
Phillips, M.; Herrera, J.; Krishnan, S.; Zain, M.; Greenberg, J.; Cataneo, R. N. Journal of
Turner, C.; Španěl, P.; Smith, D. Rapid Communications in Mass Spectrometry 2006, 20, 61-68.
(58)
526
Stone, B. G.; Besse, T. J.; Duane, W. C.; Evans, C. D.; DeMaster, E. G. Lipids 1993, 28, 705-708.
527
(59)
Turner, C.; Španěl, P.; Smith, D. Physiological Measurement 2006, 27, 13-22.
528
(60)
Stipanuk, M. H. Annual review of nutrition 1986, 6, 179-209.
529
(61)
Wu, J.; Xu, K.; Landers, J. P.; Weber, S. G. Analytical Chemistry 2013, 85, 3095-3103.
530
(62)
Garcia, R. A. G.; Hirschberger, L. L.; Stipanuk, M. H. Analytical Biochemistry 1988,
531 532
170, 432-440. (63)
533 534 535
Pitari, G.; Malergue, F.; Martin, F.; Philippe, J. M.; Massucci, M. T.; Chabret, C.; Maras, B.; Duprè, S.; Naquet, P.; Galland, F. FEBS Letters 2000, 483, 149-154.
(64)
Martínez-Lozano, P.; de la Mora, J. F. International Journal of Mass Spectrometry 2007, 265, 68-72.
ACS Paragon Plus Environment
27
Analytical Chemistry
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
536
(65)
537 538
(66)
(67)
Jordan, A.; Hansel, A.; Holzinger, R.; Lindinger, W. International Journal of Mass Spectrometry and Ion Processes 1995, 148, L1-L3.
(68)
543 544
Alonso, M.; Castellanos, M.; Sanchez, J. M. Analytical and Bioanalytical Chemistry 2010, 396, 2987-2995.
541 542
Amann, A.; Corradi, M.; Mazzone, P.; Mutti, A. Expert Review of Molecular Diagnostics 2011, 11, 207-217.
539 540
Buszewski, B.; Ulanowska, A.; Ligor, T.; Denderz, N.; Amann, A. Biomedical Chromatography 2009, 23, 551-556.
(69)
545
Poli, D.; Carbognani, P.; Corradi, M.; Goldoni, M.; Acampa, O.; Balbi, B.; Bianchi, L.; Rusca, M.; Mutti, A. Respiratory Research 2005, 6.
546
(70)
Gordon, S. M. Journal of Chromatography 1990, 511, 291-302.
547
(71)
Sanchez, J. M.; Sacks, R. D. Analytical Chemistry 2006, 78, 3046-3054.
548
(72)
Kleeblatt, J.; Ehlert, S.; Hölzer, J.; Sklorz, M.; Rittgen, J.; Baumgärtel, P.; Schubert, J.
549
Page 28 of 28
K.; Zimmermann, R. Applied Spectroscopy 2013, 67, 860-872.
550 551
FOR TOC ONLY
552
ACS Paragon Plus Environment
28