Aviv Amirav, Hongwu Jing, Eitan Atar, Sergey Cheskis, Nitzan Tzanani, Alexander Gordin and Gad Frishman (July 2015)
This is the homeland of the Pulsed Flame Photometric Detector (PFPD) and the place where it was originally developed.
A few recommendations about the optimal use of the PFPD are listed in the applications section below and a full list of over 190 PFPD publications (updated for 2008) is given at the bottom, organized by both year of publication and according to major applications.
If you are a PFPD user, or are considering it you may contact me through my E-mail: amirav@tau.ac.il
The PFPD is based on a flame source and combustible gas flow rate that cannot sustain a continuous flame operation. A combustible gas mixture of hydrogen and air (3) is continuously fed into the small pulsed flame chamber (6) (shown in Figure 1) together with the sample molecules that are eluted in the usual way from the GC column (14). The combustible gas mixture is also separately flowing (4) to a light-shielded, continuously heated, wire igniter (12). The ignited flame is propagated back to the gas source through the pulsed flame chamber (6), and is self terminated in a few milliseconds, since the pulsed flame can not propagate through the small hole of the combustor holder (5) at the bottom of the pulsed flame chamber (6). The continuous gas flow creates additional ignition after a few hundred milliseconds in a pulsed periodic fashion (~ 3Hz). The emitted light is transferred with a light pipe (8) through a broad band filter (9) and detected with a photomultiplier (10).
The PFPD is uniquely characterized by the addition of time domain information as demonstrated in Figure 2. Since the combustion of hydrocarbon molecules is very exothermic and thus fast and irreversible, their flame emission is limited to the time duration of the flame traveling along the photomultiplier window. Heteroatom species such as S2, HPO, HNO, etc. emit at the time delayed cooler yet reactive post pulsed flame conditions. Consequently, their flame emissions are electronically gated and separated in time from the hydrocarbon emission and thus provide "infinite" selectivity against hydrocarbons as well as a unique heteroatom identification capability.
A unique PFPD software was developed and is currently available in some limited forms. This PFPD View software is similar in its three dimensions concept to a GC-MS software. It stores during the chromatography time all the pulsed flame emission traces for post run reviewing and reprocessing. This software could enable the following features:
1. Serves as a screen for on-line monitoring of the PFPD emissions
for its easy
optimization.
2. Enables post run gate position optimization for higher sensitivity and infinite selectivity.
3. Provides a dual gate subtraction mode for improved
inter heteroatom selectivity.
4. Provides a dual gate response ratio for
elemental identification and multi element analysis.
5. Increases the sulfur measurement dynamic
range with a dual gate response ratio method.
6. Identifies sulfur response quenching
and helps in its elimination or reduction.
7. Provides a carbon channel
simultaneously with the sulfur selective channel.
In the PFPD, the flame chemiluminescence light emission, is pulsed and its peak intensity is largely increased. As described above, a new element specific time-domain information is added. This unique elemental kinetics is the central ingredient that contributes to the PFPD higher performance level. The emerging advantages, as demonstrated with our PFPD, are as follows:
1.
Higher Sensitivity.
The minimum detected levels of our home made PFPD are 2x10E-13
gS/sec, 1x10E-14 gP/sec and 2x10E-12 gN/sec (with 2 RMS noise level).
These sensitivities are achieved with narrowbore (0.25mm ID) capillary
columns, while with megabore columns (0.53mm ID) the sensitivity is
slightly reduced. These detection limits are much better than those of
any continuous flame FPD. In addition, due to the equimolar response of
the PFPD, these detection limits are applicable to all compounds as
they elute from the column, in contrast to standard FPD for which the
vendors use favorable samples for specifications. The superior PFPD
sensitivity is attributed to the
reduction of flame background and chemical noise due to its filtration
in time, dark current reduction due to its current gating, higher
signal brightness due to lower combustible gas flow rate and smaller
combustor volume as well as the use of broad band color glass filters.
The PFPD is equal or more sensitive than NPD in phosphorus selective
detection, without peak tailing and long term stability problems, and
it has superior selectivity against carbon and nitrogen.
The PFPD sulfur mode has similar detection limits as that of the sulfur
chemiluminescence detector (SCD), but its detection signal to noise
ratio is better at practical detection levels due
to its quadratic response. In addition, the PFPD has superior long
term stability, it is much smaller, easier to use, fully integrated
into the GC and costs much less to purchase and maintain.
2.
Improved Selectivity.
The possible separation in time of the signal from unwanted
hydrocarbon emission results in a remarkable improvement (> 10E3) of
the selectivity and thus the PFPD is a specific detector with total
discrimination against hydrocarbon compounds (selectivity over 10E7).
Please note that most vendors provide misleading FPD selectivity
specifications since in view of the FPD quadratic sulfur response it
cannot have a one number specification but rather a range of
selectivities with less than 1000 S/C near the detection limit and up
to 1E+6 at high sulfur levels. Naturally the vendors choose a high but
misleading value. The reality is that with all FPDs hydrocarbons are
observed while with the PFPD they are not observed thus one can trust
that all peaks are of sulfur compounds. The inter-heteroatom
selectivity is also markedly increased due to the
uniqueness of elemental related emission time and especially with a
dual gate subtraction software. The markedly improved selectivity
against silicon, provides stable baseline under high temperature column
bleed conditions.
3.
Lower Hydrogen Consumption.
Typically, our PFPD works with 12 ml/min hydrogen flow rate and 24
ml/min air flow rate and
without any make up gas. This hydrogen fuel saving is of special
importance in transportable GC-PFPD systems that can work on 8
ml/min hydrogen column flow rate alone, while the air is provided by a
small pump with only light air filtration due to the time separation of
hydrocarbon emission. In the laboratory, the PFPD
saves gases worth more than its price in a few years, and it is safer
as well.
4.
Nitrogen Selective Detection.
Nitrogen containing molecules
are uniquely selectively detected via their HNO flame
chemiluminescence. This detection mode provides uniform and
quantitative detection to all nitrogen compounds (except N2) including
NOx , NH3, hydrazine, amides, nitro and nitroso compounds with
good long term stability. A fast high explosives screening method
was developed and tested.
5.
Universal Heteroatom Selective Detection.
Many elements can be selectively detected with no hydrocarbon
interference's including S, P, N, As, Sn, Se, Ge, Te, Sb, Br, Ga, In,
Cu, etc. Many other elements are detected with reasonable to very good
selectivities including C, Mn, Ni, Fe, Cr, V, W, Eu, Rh, Ru, Bi, Pb,
Al, B, Si. Thus, the PFPD can serve as an alternative to the costly
atomic emission detector (AED) in many applications.
6.
Multiple Element Selective Detection Schemes.
The PFPD can simultaneously detect several element combinations such
as: S+P, P+N, S+N, S+P+N, S+P+N+As+Sn+Se+... with only a single
photomultiplier (lower cost and space). Elemental identification is
easily achieved with a dual gate response ratio method and software.
7.
Uniform Response.
All the molecular memory effects are eliminated since at the time of
delayed emission, the compounds are already completely combusted, in
analogy to the double flame photometer operation. Thus, uniform
(equimolar) S,P,N response is ensured for total elemental content
measurements and easier calibration.
8. Flexible Detector with Excellent Long Term Stability.
Since the PFPD igniter works continuously, flame out problems do not
exist. At most, when the solvent is eluted, several pulses will be
skipped and the majority of the solvent will pass the detector without
any effect. Any soot formation, if exists, is self-cleaned as the flame
propagates along the combustor walls. This property allows the GC-PFPD
to
be operated with up to 100 microliter splitless injections. This
results in a larger detection dynamic range and lower detected
concentration. Chlorinated solvent problems are eliminated through time
programming of the igniter that is off during the solvent elution time
(as with filament protection in GC-MS)
9.
Reduced Quenching.
Quenching is reduced due to the hotter post pulsed flame
conditions and through the ability to inject smaller samples
due to its improved sensitivity. In the event where it exists,
quenching may be identified by its effect on the emission time, and it
can be
corrected. Alternatively, quenching can be eliminated with 3 mm ID
combustors by the increase of the air 1 flow rate which results
in a small (less than a factor of 2) penalty in sensitivity and no
penalty
in the selectivity. A "multihole" 3 mm combustor holder was
developed and is available by the vendors, that is especially effective
in quenching reduction. With this holder, 3 mm ID combustor and 1-2
ml/min added air 1 the pulsed flame creates hot post pulsed flame
conditions that are unfavorable for the formation of the sulfur
scavenging COS hence quenching is significantly suppressed. With the
PFPD gasoline and Diesel fuel can be analyzed with one microliter split
10 injections, in contrast to FPD.
10.
Carbon Channel.
A unique reversed time separation provides a carbon channel
simultaneously with the sulfur selective detection (MDL (10E-10 gC/sec).
11.
Combination with a Pulsed FID.
A pulsed FID can be added with minor hardware addition. Simultaneous
PFID-PFPD operation is feasible with optimal detection conditions for
each mode. This combination is not available with commercial PFPDs.
12.
Increased Mass Spectrometric Identification Capabilities.
Simultaneous PFPD and MS detection via column output splitting
enables pesticide identification from single or dual MS parent or
fragment ion information. Accordingly, the PFPD marks the pesticide
elution time for optimal background subtraction and library search. At
lower concentrations a NIST sequential search is enabled that uses the
PFPD elemental information combined with the MS information on one or
two ions for the lowest concentration identification capabilities, at
the most complex
matrices.
Thus, the PFPD actually
improves the sensitivity of the MS.
1.
Sulfur Compounds in Petrochemical fluid (fuels) and
gases.
This is the most widely used PFPD application. The markedly improved
sensitivity, lack of hydrocarbon response (specificity) lower degree of
hydrocarbon induced quenching and uniform (equimolar) sulfur response makes
the PFPD a much better alternative to the FPD. While the PFPD has equivalent
sensitivity to the SCD, it is far simpler to operate and maintain, has
inherently better long term stability, is fully integrated with the GC
without additional bench space and costs much less to purchase and maintain
(gases, service). The GasPro column of Agilent (J&W) (0.32 mm ID and 1-2
ml/min Helium column flow rate) was found as a good column for sulfur gas
analysis, such as COS in propylene, H2S and other sulfur gases in natural
gas or beverage grade CO2. In this column unlike in standard thick film PDMS
columns the sulfur compounds are well separated from any potential major
coeluting hydrocarbon. Sulfur gas analysis can benefit the use of hydrogen
as the carrier gas since it enables larger volume injection through higher
(practically unlimited) carrier gas flow rate (unlike with helium) and it
results with narrower hence higher peaks. If sensitivity is critical the
sulfur doping method can be employed for about 5 times lower detection
limits and greater measurement range. Sulfur for doping air 1 at a rate of
0.1-0.2 ng/min should be used. Please read reference 6 listed below for
details. An Rtx-35 narrowbore column of Restek (0.25 mm ID) with 1 micron
film (or equivalent DB17, DB50 of VF35 VF17 with 1 micron film) was found
ideal for sulfur compound analysis in gasoline. This is since it separates
very well critical pairs such as benzene from thiophene or toluene from
methylthiophene. The thick film is important to reduce column overloading by
the hydrocarbons. With this column, up to 1 microliter can be injected with
a split ratio of 10. In order to eliminate quenching, the use of 3 mm ID
combustor, increased air 1 flow rate by 2 ml/min and gate delay of 8 msec
and width of 15 msec are recommended. Excellent sensitivity and
chromatographic separation are achieved this way as demonstrated in Figure
3. For sulfur in Diesel fuel analysis standard 0.25 mm ID columns with
0.25 micron DB5ms, VF5ms or equivalents films can be used with PFPD
conditions as for gasoline. However, the PFPD temperature should be
increased to 250C or 300C as needed to eliminate peak tailing. We note that
the PFPD can operate up to 400C unlike some FPDs that are limited to 250C.
2.
Fast Total Sulfur Determination.
The combination of the PFPD and GC instrumentation enables a fast
(under one minute) total sulfur determination method, which can be
applied to petrochemical gases and fluids, including gasoline and
Diesel fuel. This method is based on the use of a short microbore
column (1 meter, 0.1 mm ID) connected in series (with a union) with a
short megabore
column (0.5 meter, 0.53 mm ID) that is coupled with the PFPD with 3 mm
ID combustor. Standard 0.5 microliter split injection is employed with
column flow rate of 0.1 ml/min and split flow rate of 12 ml/min,
resulting in 20-25
seconds broad quasi GC peak of unseparated matrix and sulfur compounds.
The injector and column are maintained at a high temperature, typically
300C. No quenching is observed and the equimolar sulfur response
ensures the accuracy of the method. Thus, the same GC-PFPD combination
can be used for both fast total sulfur determination and sulfur
compound speciation. The detection limit in this easy to implement mode
is 5 ppm. An improved fast total sulfur GC-PFPD analyzer was developed
by us with 10 ppb detection limit and is available for collaboration
with interested vendors. p>
3.
Phosphorus Pesticides.
The PFPD superior sensitivity can be translated into reduced sample load on the
column and thus allow longer column lifetime and faster analysis with a short
narrowbore column or higher GC resolution. The use of 0.25 or 0.32 mm ID columns
is recommended since the PFPD is better optimized for lower column flow rate
operation. It can be used for pesticide analysis in "organic food items" that
requires the lowest detection limits. The PFPD can also reduce or eliminate
natural sulfur compounds interferences with the dual gate subtraction software.
(PFPD unique). These interferences are the bottleneck of trace level OP
pesticide analysis with FPD in many matrices. Very important is the PFPD ability
to also analyze a large group of sulfur containing pesticides at the required
trace concentrations (in contrast to FPD). The PFPD can also uniquely determine
the P/S elemental ratio in pesticides that contain both atoms. The PFPD has a
sensitivity similar to that of NPD but without peak tailing and long term
stability problems and it has superior selectivity against hydrocarbon and
nitrogen compounds. The PFPD is ideally coupled with the MS for simultaneous
PFPD-MS pesticide analysis as described in detail in reference 12 listed below.
The use of the ChromatoProbe for GC sampling and intra GC injector thermal
desorption eliminates the need for extraction and effectively utilizes the
enhanced PFPD sensitivity that compensates for the lack of concentration with
the blending only procedure. Extensive PFPD pesticide analysis information can
be found in the PFPD list of papers/references below.
4.
Sulfur Pesticides.
About 20% of the EPA list of pesticides contain a sulfur atom without
phosphorus. Usually they are detected through their nitrogen atoms using
NPD, but the natural presence of a large multitude of natural nitrogen
compounds hampers this detection mode, so their monitoring via the sulfur
mode should be preferred. The PFPD is the only detector in the market that
has the required sensitivity for sulfur pesticides, which can also monitor
phosphorus pesticides. The S and P pesticides can also be monitored
simultaneously, and the S/P atom ratio information is provided for
pesticides that contain both S and P atoms. Nitrogen pesticides can also be
monitored using the PFPD in its nitrogen mode but with some sensitivity
limitations. In addition to sulfur pesticides such as Endosulfane,
Metribuzin, Folpet, Ametryn, Prometrin, Butylate, Propargite and
Ethylenethiourea, important sulfur carbamates can be analyzed including
Aldicarb, Methomyl and Methyocarb. A special method was developed for the
analysis of these thermally labile pesticides based on using a short (4
meter) column with 0.25 mm ID, 5 ml/min He column flow rate and injection at
140C injector temperature (preferably a PTV injector) with an empty liner.
Please contact me for details if you wish to analyze these or other
thermally labile carbamate pesticides and I will be happy to Email you a
power point presentation on this application.
5.
Chemical Warfare Agents (CWA) Detection.
The enhanced sensitivity, total elimination of hydrocarbon
interferences, much lower
gas consumption, ability to monitor all the range of CWA, including
arsenic and/or nitrogen containing compounds and ability to use
chlorinated solvents make the PFPD the ideal detector of choice for
this purpose. The multi element selective detection capability with
only one photomultiplier tube (PMT) makes it also less
expensive and smaller than FPD with two PMT's. Several multiple
element detection schemes can be chosen such as: S, P, As, N, (S+P),
(P+N), (As+P), (As+N), (S+P+As), (P+As+N), (S+P+As+N). Many PFPDs (over
60) are being used for this application worldwide. br>
FoFor further information on the use of the PFPD for CWA analysis with
our new miniaturized system please read reference 17 or go to Fast GC-PFPD
System for Field Analysis of Chemical Warfare Agents
6.
Sulfur Drugs.
While the majority of drugs contain nitrogen atoms, about 15% of
them also contain a sulfur
atom. Due to the presence of large amount of natural nitrogen
compounds in biofluids such as plasma or urine extracts, sulfur
selective detection should be preferred for the selective detection of
sulfur drugs. The PFPD sulfur sensitivity is similar or better
than that of the NPD nitrogen sensitivity and thus it is compatible
with the current drug research requirements. p>
7.
Organotin Compounds in the Environment, Sea Water and Fish Products.
The excellent tin sensitivity and selectivity of the PFPD make it an ideal
organotin selective detector. The PFPD is also characterized by good long term
stability for tin due to the self-cleaning mechanism of the combustion zone. The
PFPD was found as the most sensitive tin selective GC detector. Tin analysis
requires a BG12 filter (sulfur filter) which provides the best sensitivity, gate
delay of 4 msec, gate width 2-3 msec (for greater LDR), 3 mm combustor ID and
gases as in the phosphorus mode. It is recommended to keep the PFPD on at all
time for lowest noise. High base temperature such as 350C should be employed to
reduce the PFPD tin peak tailing and in the Varian PFPD the aluminum thermal
insulation cup should be mounted. The dual gate subtraction method can be used
to eliminate sulfur interference. Please read about this application references
number 10 (ours with tin analysis details), and the other 19 tin-PFPD analysis
papers listed below in the tin analysis papers section. I am familiar in person
and through Emails with over 16 PFPD tin users and a few of them reported about
0.2 pg tin compound detection limit that is about 100 times more sensitive than
FPD, with excellent long term stability.
8. Arsenic Compounds in Petroleum Streams.
The PFPD has a very good arsenic selective detection capability that makes it
very useful in the monitoring of catalyst poisoning gases such as arsine and
various methyl arsine. The PFPD can also detect simultaneously AsH3 , PH3 and
COS (SilicaPLOT or GasPro columns). The optimal As selective detection mode
requires R5070 PMT, RG695 filter, 3 mm ID combustor and gate position and gases
as in the sulfur mode. With the standard PMT As can be detected with any filter
but with slightly reduced sensitivity. Please read our reference 10 and the
recent reference 26 and 37 for more details.
9.
Manganese in Gasoline.
The PFPD can selectively detect the fuel additive
methylcyclopentadienylmanganese tricarbonyl (MMT) at sub ppm levels (far below
the 80 ppm allowed in Canada). A Varian application note on this can be found at
the Varian list of application notes. Figure 41 in the PFPD blue book also
demonstrates this application and a few PFPDs are in service for this
application. (please read Ref 10 for details)
10.
General Organometallic Detection.
The PFPD can serve as an alternative to the AED in many organometallic selective
detection applications. It can also be used instead of atomic absorption for the
simultaneous detection of hydride forming elements (As, Sb, Bi, Te, Se, etc).
11.
General use in the Semiconductor Industry.
The PFPD can detect all the elements in use by this industry including P(PH3),
S(H2S, SO2), B(B2H6), As(AsH3), Si(SiH4, SiCl4), Ge(GeH4), N(NH3, N2H2),
Ga(Ga(CH3)3), In(In(CH3)3) and hydrocarbons.
12.
Vehicle Exhaust Emission Analysis.
The PFPD can uniquely simultaneously detect NO, NO2 and SO2, H2S in
various applications of exhaust emission analysis.
13.
Beverage Grade CO2 Analysis.
The PFPD can uniquely simultaneously selectively detect SO2,
mercaptanes and NH3 in this gas. (SilicaPLOT or GasPro 0.32 mm ID
columns, BG3 filter for S+N mode). Many PFPDs are being used for the
detection of sulfur gases in beverage grade CO2 and an application note
is available upon request.
14.
Coffee (and Beer) Aroma Analysis.
The PFPD can be very effective in coffee production process control through the
analysis of sulfur compounds in its aroma fraction (see Wang et al.
Chromatographia 17, 411 (1983)). The PFPD can also selectively detect the
nitrogen compounds in coffee aroma or powder. An application note on this
subject is available on request. Several PFPDs are routinely used in this
application by the industry. The PFPD is also used by the industry for the
analysis of trace levels of sulfur compounds in beer (reference 18)
15.
Drugs and Organic Synthetic Applications.
The PFPD uniform response enables the quantification of chemical
reaction products. The comparison with FID provides N/C molecular
content ratio. /p>
16.
Explosive Screening and Analysis.
In its nitrogen mode, the PFPD can selectively detect all the
explosives including the nitrate esters (unlike NPD). A unique high
injection temperature mode enables fast explosive screening via their
injector pyrolysis into NO that elutes in a few seconds. The use of a
short column with
high column flow rate enables the analysis of the full range of
explosives including RDX, PETN and Tetryl. An application note on
this subject is available on request. /p>
In the analysis of trace levels of pesticides in complex matrices, mass spectral library identification is often hampered by the co-elution of several matrix compounds.
The PFPD enables simultaneous sulfur and phosphorus information, including the S/P ratio for a given pesticide to supplement and complement mass spectral information.
Simultaneous PFPD-MS analysis is performed with column effluent splitting between these two detectors. The resulting PFPD chromatograms are always much simpler due to its selectivity and are further characterized by better sensitivity than that of the MS. Accordingly, the PFPD chromatogram serves as a marker for the exact elution time of the suspected pesticide. At this exact elution time, the resulting mass spectra are examined for unique high mass peaks and a precise background subtraction is performed for improved library identification. If no definite identification is achieved, reconstructed single ion mass chromatograms are performed on suspected major ions and confirmed with the PFPD chromatogram. A sequential search is then performed with the NIST library. The presence of P and or S atoms is introduced and the suspected two major ion mass peaks are included with a low estimate of their relative abundance. Under these conditions, the library search provides the correct pesticide identification, at considerably lower concentration than that achievable with a standard GC-MS analysis.
If only single ion information is available as in the single ion monitoring mode, the NIST library sequential search is operated with this information and information on both P and S is introduced. The incorporation of one major ion and two heteroatoms P and S information enables the proper library identification, at up to an order of magnitude lower concentration than with the MS alone. Note that the majority of organophosphorus pesticides contains both P and S. Major anticipated applications of this novel PFPD-MS approach are pesticide analysis, CWA detection and unknown sulfur compound identification in complex matrices such as coffee, tea and various food items. An unexpectedly large portion of the PFPDs are sold with GC-MS systems. The PFPD-MS method is further explained in details in references 12.
AA unique device for extract-free sampling was developed by us to supplement and complement the PFPD. It is available from Varian/Bruker with the name ChromatoProbe and by Agilent with the name Thermal Separation Probe (TSP). This novel device and method (USA and Japan patents) is separately described in our ChromatoProbe and SnifProbe page. It is based on sampling in a micro vial and intra GC injector thermal desorption. It was extensively tested in the analysis of pesticides in fruits, vegetables and other food items as well as drugs in urine and hair. This device considerably simplifies sample preparation, enables faster analysis and can further improve the detection sensitivity. It is also very useful in combination with other detectors and as an alternative to a "direct probe" for GC-MS. Recently its use was extended for field gas and airborne sample collection and analysis with the addition of the SnifProbe device.
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2. E. Atar, S. Cheskis and A. Amirav, "Pulsed Flame - A Novel Concept for Molecular Detection", Anal. Chem., 63, 2061-2064 (1991).
3. S. Cheskis, E. Atar and A. Amirav, "Pulsed Flame Photometer - A Novel Gas Chromatography Detector", Anal. Chem., 65, 539-555 (1993).
4. N. Tzanani and A. Amirav, "The Combined Pulsed Flame Photometric Ionization Detector", Anal. Chem., 67, 167-173 (1995). ).
5. L. Kalontarov, H. Jing, A. Amirav and S. Cheskis, "Mechanism of Sulfur Emission Quenching in Flame Photometric Detectors", J. Chromatog. A. 696, 245-256 (1995).
6. A. Amirav and H. Jing, "Pulsed Flame Photometer Detector for Gas Chromatography", Anal. Chem. 67, 3305-3318 (1995).
7. S. Cheskis, "Mechanism of Sulfur Chemiluminescence Emission in Pulsed Flames" Combustion and Flames 100, 550-558 (1995).
8. I. Brailovsky I, S. Cheskis, and G. Sivashinsky "Dynamical aspects of pulsed flames" Combust. Sci. Technol. 118, 49-62 (1996).
9. H. Jing and A. Amirav, "Pesticides Analysis with the Pulsed Flame Photometric Detector and a Direct Sample Introduction Device", Anal. Chem. 69, 1426-1435 (1997).
10. H. Jing and A. Amirav, "Pulsed Flame Photometric Detector - A Step Forward Towards Universal Heteroatom Selective Detection", J. Chromatog. A. 805, 177-215 (1998).
11. J. A. Jacobsen, F. Stuer-Lauridsen and G. Pritzl, "Organotin Speciation in Environmental Samples by Capillary Chromatography and Pulsed Flame Photometric Detection (PFPD)" Appl. Organometallic. Chem., 11, 737-741 (1997).
12. A. Amirav and H. Jing, "Simultaneous Pulsed Flame Photometric and Mass Spectrometric Detection for Enhanced Pesticide Analysis Capabilities", J. Chromatog. A. 814, 133-150 (1998).
13. R. D. Snelling, "Analysis of organophosphorus pesticides using gas chromatography with pulsed flame photometric detection" Am Lab 30: (4) 32C-+ FEB 1998.
14. J. L. M Vidal, F. J. E Gonzalez, M. M. Galera and M. L. C. Cano "Diminution of chlorpyrifos and chlorpyrifos oxon in tomatoes and green beans grown in greenhouses" J. Agri. Food. Chem. 46, 1440-1444 (1998).
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17. Gad Frishman and Aviv Amirav, "Fast GC-PFPD System for Field Analysis of Chemical Warfare Agents" Field. Anal. Chem. Technol. 4, 170-194 (2000).
18. P. G. Hill and R. M. Smith, "Determination of sulphur compounds in beer using headspace solid-phase microextraction and gas chromatographic analysis with pulsed flame photometric detection" J. Chromatog. A. 872, 203-213 (2000).
19. S. Dagan, "Comparison of gas chromatography-pulsed flame photometric detection-mass spectrometry, automated mass spectral deconvolution and identification system and gas chromatography-tandem mass spectrometry as tools for trace level detection and identification" J. Chromatog. A. 868, 229-247 (2000).
20. X. S. Chai, P. H. Liu, J. Y. Zhu, "Analysis of volatile organic sulphur compounds in kraft liquors by full evaporation headspace gas chromatography" J. Pulp. Pap. Sci. 26, 167-172 (2000).
21. U. Thuss, P. Popp, C. Ehrlich and W. D. Kalkoff, "Identification and quantification of thiaarenes in the flue gas of lignite-fired domestic heating" J. High. Res. Chromatog. 23 457-473 (2000).
22. Alexander Gordin and Aviv Amirav, "SnifProbe - A New Method and Device for Vapor and Gas Sampling" J. Chromatog. A. 903, 155-172 (2000).
23. C. Bancon-Montigny, G. Lespes and M. Potin-Gautier, "Improved
routine speciation of organotin compounds in environmental samples by
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24. H. L. Chiang, J.H. Tsaib, D.H. Changb and F.T. Jengc,
"Diffusion of hydrogen sulfide and methyl mercaptan onto microporous
alkaline activated carbon" Chemosphere 41, 1227-1232 (2000).
25. F. Rota and R. Prins, "Mechanism of the hydrodenitrogenation
of o-toluidine and methylcyclohexylamine over NiMo/Al2O3" Topics in
Catalysis 11-12 327–333 (2000)
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29. G. Frishman, A. Amirav and H. Barak, "Pressure and Gas Composition Effects on the Operation of the Pulsed Flame Photometric Detector" Israel. J. Chem. 41, 91-97 (2001).
30. L. V. Podhorniak, J. F. Negron and F. D. Griffith "Gas chromatography with pulsed flame photometric detection multiresidue method for organophosphate pesticide and metabolite residues at the parts-per-billion level in representative commodities of fruit and vegetable crop groups" J. AOAC. Int. 84, 873-890 (2001).
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32. J. Westa, B. P. Williamsb, N. Youngb, C. Rhodesa and G. J.
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34. M. E. H. Torres, F. J. E. Gonzalez, M. L. C. Cano, M. M Frias and J. L. M. Vidal. "Residues of methamidofos, malathion, and methiocarb in greenhouse crops" J. Agri. Food. Chem 50, 1172-1177 (2002).
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39. K. Beiner, P. Popp and R.Wennrich, "Selective enrichment of sulfides, thiols and methylthiophosphates from water samples on metal-loaded cation-exchange materials for gas chromatographic analysis" J. Chromatog. A. 968, 171-176 (2002).
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41. M. Kawarai, T. Shirasaki and K. Mizuishi "Analysis of organotin compounds in seawater using GC/pulsed flame photometric detection" Bunseki Kagaku 51, 959-964 (2002).
42. M. Bech, "Imposex and tributyltin contamination as a
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45. S. D. Archer, F. J. Gilberta P. D. Nightingalea, M. V. Zubkova, A. H. Taylora, G. C. Smithb and P. H. Burkilla "Transformation of dimethylsulphoniopropionate to dimethyl sulphide during summer in the North Sea with an examination of key processes via a modelling approach" Deep Sea Research Part II: Topical Studies in Oceanography Volume 49, Issue 15 , Pages 3067-3101 (2002).
46. J. G. Dreher, R. L. Rouseff, M. Naim "GC-olfactometric characterization of aroma volatiles from the thermal degradation of thiamin in model orange juice" J. Agr. Food. Chem. 51, 3097-3102 (2003).
47. A. F.L. Godoi, R. C. Montone and M. Santiago-Silva "Determination of butyltin compounds in surface sediments from the Sao Paulo State coast (Brazil) by gas chromatography–pulsed flame photometric detection" J. Chromatog. A. 985 205-210 (2003).
48. H. Mei, B. W. Mei and T. F. Yen "A new method for obtaining
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49. M. F. Valim, R. L. Rouseff, J. M. Lin "Gas
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50. M. Le Gac, G. Lespes and M. Potin-Gautier "Rapid determination of organotin
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51. J. A. Muñoz, E. F. González, L. E. García-Ayuso, A. G. Casado and L.
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52. F. Lestremau, V. Desauziers, J. C. Roux and J. L. Fanlo "Development of a
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53. A. M. Lisovac and D. Shooter "Volatiles from sheep wool and the modification
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54. J. Strand, J. A. Jacobsen, B. Pedersen and Å Granmo "Butyltin compounds in
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55. A. F. L. Godoi, R. Favoreto, M. Santiago-Silva "GC Analysis of
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56. P. X. Xu, D. X. Yuan, S. M Zhong and Q. M. Lin "Determination of
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57. L. Chambers and M.L. Duffy "Determination of Total and Speciated Sulfur
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58. A. De Nino, F. Santelli, N. Servidio, G. Sindona and A. Tagarelli
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59. E. Tomaszewska and V. R. Herbert "Analysis of O,S-Dimethyl Hydrogen
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60. J. Strand and G. Asmund "Tributyltin accumulation and effects in marine
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61. F. Lestremau, V. Desauziers and J. L. Fanlo "Headspace SPME Followed by
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62. E. Ueno, H. Oshima, I. Saito, H. Matsumoto and H. Nakazawa "Determination of
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63. G. Lespes, C. Marcic, I. Le Hecho, M. Mench and M. Potin-Gautier "Speciation
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64. K. F. Schulbach, R. L. Rouseff and C. A. Sims "Changes in Volatile Sulfur
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65. X. T. Fan, C. H. Sommers and K. J. B. Sokorai "Ionizing Radiation and
Antioxidants Affect Volatile Sulfur Compounds, Lipid Oxidation, and Color of
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66. R. Bentley and T. G. Chasteen "Environmental VOSCs––Formation and
Degradation of Dimethyl Sulfide, Methanethiol and Related Materials"
Chemosphere, 55, 291-317 (2004).
67. Ch. Bancon-Montigny, G. Lespes and M. Potin-Gautier "Organotin Survey in the
Adour–Garonne Basin" Water Research 38, 933-946 (2004).
68. Y. Zhao, P. Kukula and R. Prins, "Investigation of the Mechanism of the
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69. E. Soboleva and A. Ambrus "Application of a system suitability test for
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70. K. H. Kim, H. Swanb, Z. H. Shonc, G. Leed, J. Kime and C. H. Kangf
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during the Spring of 2001" Chemosphere 54, 515-526 (2004).
71. S. H. Tseng, Y. W. Lo, P. C. Chang, S. S. Chou and H. M. Chang "Simultaneous
quantification of glyphosate, glufosinate, and their major metabolites in rice
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72. M. Levasseur, M. Scarratt, S. Roy, D. Laroche, S. Michaud, G. Cantin, M.
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73. M. Bravo, G. Lespes, I. D. Gregori, H. Pinochet and M. Potin-Gautier,
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74. J. Ramaprasad, M. Y. Tsai, K. Elgethun, V. R. Hebert, A. Felsot, M. G. Yost
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75. K. C. Li and D. Shooter, "Analysis of sulfur-containing compounds in ambient
air using solid-phase microextraction and gas chromatography with pulsed flame
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76. X. Ma, S. Velu, J. H. Kim and C. Song "Deep desulfurization of gasoline by
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ppm-level sulfur quantification for fuel cell applications" Applied Catalysis B:
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77. A. Corma, J. Y. Chane-Ching, M. Airiau and C. Martínez "Synthesis and
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SiO2–CeO2 mesostructured composite materials and their application for the
removal of sulfur compounds from gasoline". J. Catalysis 224, 441-448 (2004).
78. Z. H Shon, K. H. Kim, K. N. Bower, G. Lee and J. Kim "Assessment of the
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79. T. J. Campbell, A. H. Shaaban, F. H. Holcomb, R. Salavani and M, J. Binder
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81. X. Fan, "Involvement of Volatile Sulfur Compounds in Ionizing
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82. A. C. Almeida, A. D. R. Wagener, C. B. Maia. and N. Miekeley, "Speciation of
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83. M. J. van der Schans, M. Polhuijs, C. van Dijk, C. E. A. M. Degenhardt, K.
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exposure to nerve agents: analysis of phosphofluoridates originating from
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84. H. M. Burbank and M. C.Qian "Volatile sulfur compounds in Cheddar cheese
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85. X. L. Ma, S. Velu, J. H. Kim and C. S. Song, "Deep desulfurization of
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86. Z. H. Shon, K. H. Kim, H. Swan, G. Lee and Y. K. Kim, "DMS photochemistry
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87. K. H. Kim, Y. J. Choi, E. C. Jeon and Y Sunwoo "Characterization of
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88. M. Leermakers, J. Nuyttens and W. Baeyens "Organotin analysis by gas
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89. J. P. Le Harle and B. Bellier "Optimisation of the selectivity of a pulsed
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91. M, Leermakers, J. Nuyttens and W. Baeyens "Organotin analysis by gas
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92. W. E. Lambert, M. Lasarev, J. Muniz, J. Scherer, J. Rothlein, J. Santana,
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95. Y. Fang and M. C. Qian, "Sensitive quantification of sulfur compounds in
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96. G. Karvaly, A. Gachalyi and J. Furesz, Quantitative analysis of
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99. H. Y. Wang, Y. D. Wang, X. F. Wang and H. M. Hao, "Determination of Lewisite in ambient air and water by solid phase microextraction-pulsed flame photometric detector" Chinese J. Anal. Chem. 33, 1479-1482 (2005).
100. K. H. Kim, "Some insights into the gas chromatographic determination of reduced sulfur compounds (RSCs) in air" Environ. Sci. Technol. 39, 6765-6769 (2005).
101. J. Strand, M. M. Larsen and C. Lockyer, "Accumulation of organotin compounds and mercury in harbour porpoises (Phocoena phocoena) from the Danish waters and West Greenland" Sci. Total. Environ. 350, 59-71 (2005).
102. K. H. Kim, D. W. Ju and S. W. Joo, "The evaluation of recovery rate associated with the use of thermal desorption systems for the analysis of atmospheric reduced sulfur compounds (RSC) using the GC/PFPD method" Talanta, 67, 955-959 (2005).
103. G. P. Yang, M. Levasseur, S. Michaud and M. Scarratt, "Biogeochemistry of dimethylsulfide (DMS) and dimethylsulfoniopropionate (DMSP) in the surface microlayer and subsurface water of the western North Atlantic during spring" Marine. Chem. 96, 315-329 (2005).
104. Z. H. Shon, K. H. Kim, E. C. Jeon, M. Y. Kim, Y. K. Kim and S. K. Song, "Photochemistry of reduced sulfur compounds in a landfill environment" Atm. Environ. 39, 4803-4814 (2005).
105. O. Elizalde-Solis and L. A. Galicia-Luna, "Solubility of thiophene in carbon dioxide and carbon dioxide + 1-propanol mixtures at temperatures from 313 to 363 K" Fluid. Phase. Equilibria. 230, 51-57 (2005).
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107. M. Hesta, E. Hoornaert, A. Verlinden and G. P. J. Janssens "The effect of oligofructose on urea metabolism and faecal odour components in cats" J. Animal. Physiol. Animal. Nutri. 89, 208 (2005).
108. C. Marcic, G. Lespes and M. Potin-Gautier, " "Pressurised solvent extraction for organotin speciation in vegetable matrices" Anal. Bioanal. Chem. 382, 1574-1583 (2005).
109. K. Karan, A. K. Mehrotra and L. A. Behie, "Thermal Decomposition Of Carbonyl Sulfide At Temperatures Encountered In The Front End Of Modified Claus Plant"Chem. Eng. Commun. 192. 370-385 (2005).
110. B. Yu, P. Xu, Q. Shi and C. Ma, "Deep Desulfurization of Diesel Oil and Crude Oils by a Newly Isolated Rhodococcus erythropolis Strain" Appl. Environ. Microbiol. 72, 54-58 (2006).
111. M. El Ati-Hellal, G. Lespes and M. Dachraoui, "Determination of organotins in aquatic plants by headspace SPME followed by GC-PFPD determination" Int. J. Environ. Anal. Chem. 86, 733-742 (2006).
112. P. A. Vazquez-Landaverde, J. A. Torres and M. C. Qian, "Quantification of trace volatile sulfur compounds in milk by solid-phase microextraction and gas chromatography-pulsed flame photometric detection" J. Dairy. Sci. 89, 2919-2927 (2006).
113. K. H. Kim, " A dual-mode GC analysis of reduced sulphur compounds in air over a wide concentration range" Int. J. Environ. Anal. Chem. 86, 805-817 (2006).
114. K. H. Kim, "The properties of calibration errors in the analysis of reduced sulfur compounds by the combination of a loop injection system and gas chromatography with pulsed flame photometric detection" Anal. Chim. Acta. 566, 75-80 (2006).
115. K. H. Kim, G. H. Choi, Y. J. Choi, H. N. Song, H. S. Yang and J. M. Oh, "The effects of sampling materials selection in the collection of reduced sulfur compounds in air" Talanta, 68, 1713-1719 (2006).
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667-672 (2006).
25. S. H. Tseng, Y. J. Lin, H.
F. Lee, S. C. Su, S. S. Chou and D. F. Hwang, "A
multiresidue method for determining 136 pesticides and
metabolites in fruits and vegetables: Application of
macroporous diatomaceous earth column" J. Food Drug.
Anal. 15, 316-324 (2007).
26. A. Bradman et. Al.
"Pesticides and their Metabolites in the Homes and Urine
of Farmworker Children Living in the Salinas Valley, CA"
J. Exposure Sci. and Environ. Epidemiology 17, 331–349
(2007).
27. G. J. Daglish and H. Pavic "Effect of phosphine dose
on sorption in wheat" Pest Management Science 64, 513 –
518 (2008).
28. G. De Nola, J. Kibby and W.
Mazurek Determination of ortho-cresyl phosphate isomers
of tricresyl phosphate used in aircraft turbine engine
oils by gas chromatography and mass spectrometry" J.
Chromatogr. A 1200, 211-216 (2008).
Chemical Warfare Agent (CWA)
Analysis with the PFPD
2. M. J. van der Schans, M. Polhuijs, C. van Dijk, C. E.
A. M. Degenhardt, K. Pleijsier, J. P. Langenberg and H.
P. Benschop, "Retrospective detection of exposure to
nerve agents: analysis of phosphofluoridates originating
from fluoride-induced reactivation of phosphylated
BuChE" Archives of Toxicology 78, 508-524 (2004).
3. J. P. Le Harle and B. Bellier
"Optimisation of the selectivity of a pulsed flame
photometric detector for unknown compound screening" J.
Chromatog. A. 1087, 124-130 (2005).
4. G.
Karvaly, A. Gachalyi and J. Furesz, Quantitative
analysis of the sulfur mustard hydrolysis product
thiodiglycol (2,2 '-sulfobisethanol) in in vivo
microdialysates using gas chromatography coupled with
pulsed flame photometric detection" J. Chromatog Sci 43,
319-323 (2005).
5. H. Y. Wang, Y.
D. Wang, X. F. Wang and H. M. Hao, "Determination of
Lewisite in ambient air and water by solid phase
microextraction-pulsed flame photometric detector"
Chinese J. Anal. Chem. 33, 1479-1482 (2005).
6. G.
Amita, L. Gaidukov, R. Adani, S. Yishay, G. Yacov, M.
Kushnir, S. Teitlboim, M. Lindenbaum, P. Bel, O.
Khersonsky, D. S. Tawfik, and H. Meshulam "Enhanced
stereoselective hydrolysis of toxic organophosphates by
directly evolved variants of mammalian serum
paraoxonase" FEBS JOURNAL 273, 1906-1919 (2006).
7. T. W. Sawyer et. al.
"pH-dependent toxicity of sulphur mustard in vitro"
Toxicology and Applied Pharmacology 221, 363-371 (2007).
8. P. Nelson, A. Burczyk and
T.W. Sawyer, "Lack of a role for creatine phosphate
kinase in sulphur mustard-induced cytotoxicity" Human &
Experimental Toxicology, 26, 891-897 (2007).
9. F. J. Schenck, A. N. Brown,
L. V. Podhorniak, A. Parker, M. Reliford and J. W. Wong
"A Rapid Multiresidue Method for Determination of
Pesticides in Fruits and Vegetables by Using
Acetonitrile Extraction/Partitioning and Solid-Phase
Extraction Column Cleanup" J. AOAC Int. 91, 422-438
(2008).
Organotin Compound Analysis with the PFPD
2. J. A. Jacobsen, F. Stuer-Lauridsen and G. Pritzl,
"Organotin Speciation in Environmental Samples by
Capillary Chromatography and Pulsed Flame Photometric
Detection (PFPD)" Appl. Organometallic. Chem., 11,
737-741 (1997).
3. C. Bancon-Montigny, G. Lespes
and M. Potin-Gautier, "Improved routine speciation of
organotin compounds in environmental samples by pulsed
flame photometric detection"J. Chromatog. A. 896,
149-158 (2000).
4. S. Aguerre, G. Lespes, V.
Desauziers and M. Potin-Gautier, "Speciation of
organotins in environmental samples by SPME-GC:
comparison of four specific detectors: FPD, PFPD,
MIP-AES and ICP-MS" J. Anal. Atom. Spectros. 16, 263-269
(2001).
5. J. L. Gomez-Ariza, F. Mingorance, A. Velasco-Arjona,
I. Giraldez, D. Sanchez-Rodas and E. Morales,
"Determination of methyltin species in sediments using a
pervaporation-gas chromatographic approach" Appl.
Organometallic. Chem. 16, 210-215 (2002).
6. S. Simon, M. Bueno, G.
Lespes, M. Mench and M. Potin-Gautier "Extraction
procedure for organotin analysis in plant matrices:
optimisation and application" Talanta. 57, 31-43 (2002).
7. M. Kawarai, T. Shirasaki and
K. Mizuishi "Analysis of organotin compounds in seawater
using GC/pulsed flame photometric detection" Bunseki
Kagaku 51, 959-964 (2002).
8. M. Bech, "Imposex and
tributyltin contamination as a consequence of the
establishment of a marina, and increasing yachting
activities at Phuket Island, Thailand" Env. Poll. 117,
421-429 (2002).
9. A. F.L. Godoi, R. C. Montone
and M. Santiago-Silva "Determination of butyltin
compounds in surface sediments from the Sao Paulo State
coast (Brazil) by gas chromatography–pulsed flame
photometric detection" J. Chromatog. A. 985 205-210
(2003).
10. M. Le Gac, G. Lespes and M. Potin-Gautier "Rapid
determination of organotin compounds by headspace
solid-phase microextraction" J. Chromatog. A. 999,
123-134 (2003).
11. J. Strand, J. A. Jacobsen,
B. Pedersen and Å Granmo "Butyltin compounds in sediment
and molluscs from the shipping strait between Denmark
and Sweden" Environmental Pollution 124, 7-15 (2003).
12. A.
F. L. Godoi, R. Favoreto, M. Santiago-Silva "GC Analysis
of Organotin Compounds Using Pulsed Flame Photometric
Detection and Conventional Flame Photometric Detection"
Chromatographia 58, 97-101 (2003).
13. J.
Strand and G. Asmund "Tributyltin accumulation and
effects in marine molluscs from West Greenland"
Environmental Pollution 123, 31-37 (2003).
14. G.
Lespes, C. Marcic, I. Le Hecho, M. Mench and M.
Potin-Gautier "Speciation of organotins in French beans
and potatoes cultivated on soils spiked with solutions
or amended with a sewage sludge" Electronic Journal of
Environmental Agricultural ands Food Chemistry 2004.
15. Ch. Bancon-Montigny, G.
Lespes and M. Potin-Gautier "Organotin Survey in the
Adour–Garonne Basin" Water Research 38, 933-946 (2004).
16. M. Bravo, G. Lespes, I. D.
Gregori, H. Pinochet and M. Potin-Gautier,
"Identification of sulfur interferences during organotin
determination in harbour sediment samples by sodium
tetraethyl borate ethylation and gas
chromatography-pulsed flame photometric detection" J.
Chromatog. A. 1046, 217-224 (2004).
17. A.
C. Almeida, A. D. R. Wagener, C. B. Maia. and N.
Miekeley, "Speciation of organotin compounds in sediment
cores from Guanabara Bay, Rio de Janeiro (Brazil) by gas
chromatography-pulsed flame photometric detection".
Appl. Oganometallic Chem.18, 694-704 (2004).
18. M. Leermakers, J. Nuyttens
and W. Baeyens "Organotin analysis by gas
chromatography-pulsed flame-photometric detection
(GC-PFPD)" Anal. Bioanal. Chem. (In Press) (2005)
19. N.
Mzoughi, G. Lespes, M. Bravo, M. Dachraoui and M.
Potin-Gautier "Organotin speciation in Bizerte lagoon
(Tunisia)" Science of The Total Environment, 349,
211-222 (2005).
20. M, Leermakers, J. Nuyttens
and W. Baeyens "Organotin analysis by gas
chromatography-pulsed flame-photometric detection
(GC-PFPD)" Anal. Bioanal. Chem. 381, 1272-1280 (2005).
21. M. Bravo, G. Lespes, I. De
Gregori, H. Pinochet and M. P. Gautier, "Determination
of organotin compounds by headspace solid-phase
microextraction-gas chromatography-pulsed
flame-photometric detection (HS-SPME-GC-PFPD)" Anal.
Bioanal. Chem. 383, 1082-1089 (2005).
22. J.
Strand, M. M. Larsen and C. Lockyer, "Accumulation of
organotin compounds and mercury in harbour porpoises
(Phocoena phocoena) from the Danish waters and West
Greenland" Sci. Total. Environ. 350, 59-71 (2005).
23. C.
Marcic, G. Lespes and M. Potin-Gautier, " "Pressurised
solvent extraction for organotin speciation in vegetable
matrices" Anal. Bioanal. Chem. 382, 1574-1583 (2005).
24. M.
El Ati-Hellal, G. Lespes and M. Dachraoui,
"Determination of organotins in aquatic plants by
headspace SPME followed by GC-PFPD determination" Int.
J. Environ. Anal. Chem. 86, 733-742 (2006).
25. C. Marcic, I. Le Hecho, L.
Denaix and G. Lespes, "TBT and TPhT persistence in a
sludged soil" Chemosphere 65, 2322-2332 (2006).
26. T.
Zuhani, G. Lespes, R. Milacic, J. Scancar and M
Potin-Gautier "Influence of the soil matrices on the
analytical performance of headspace solid-phase
microextraction for organotin analysis by gas
chromatography-pulsed flame photometric detection" J.
Chromatogr. A. 1132, 234-240 (2006).
27. C. A. Impellitteri O. Evans
and B. Ravel, "Speciation of organotins in polyvinyl
chloride pipe via X-ray absorption spectroscopy and in
leachates using GC-PFPD after derivatisation" J.
Environ. Monitor 9, 358-365 (2007).
28. C. A. Impellitteri, O. Evans
and B. Ravel, "Speciation of organotins in polyvinyl
chloride pipe via X-ray absorption spectroscopy and in
leachates using GC- PFPD after derivatisation" J.
Environ. Monitor. 9, 358-365 (2007).
29. C. A. Impellitteri, O. Evans
and B. Ravel, "Speciation of organotins in polyvinyl
chloride pipe via X-ray absorption spectroscopy and in
leachates using GC-PFPD after derivatisation" J.
Environ. Monit., 9, 358-365 (2007).
30. J.
Heroult, T. Zuliani, M. Bueno, L. Denaix and G. Lespes
"Analytical advances in butyl-, phenyl- and octyltin
speciation analysis in soil by GC-PFPD" Talanta, 75,
486-493 (2008).
31. T. Zuliani, G. Lespes, R.
Milačič, J. Ščančar and M. Potin-Gautier "Comprehensive
study of the parameters influencing the detection of
organotin compounds by a pulsed flame photometric
detector in sewage sludge" J. Chromatogr. A, 1188,
281-285 (2008).
32. J. Heroult, M. Bueno, M.
Potin-Gautier and G. Lespes, "Organotin speciation in
French brandies and wines by solid-phase microextraction
and gas chromatography—Pulsed flame photometric
detection" J. Chromatogr. A, 1180, 122-130 (2008).
33. J. F. Felizzola, A. D. R.
Wagener, A. C. Almeida and W. O. Lin, "Butyltin
speciation in sediments from Todos os Santos Bay (Bahia,
Brazil) by GC-PFPD" QUIMICA NOVA 31 89-93 (2008).
34. Y. F. Zhao, K. X. Zhao and
Y. N. Wu, "Determination of organotins in aquatic food
by gas chromatography with pulsed flame photometric
detection" J. AOAC Int. 91, 653-659 (2008).
35. S. Dubascoux, J. Heroult, I.
L. Hecho, M. Potin-Gautier and G. Lespes, "Evaluation of
a combined fractionation and speciation approach for
study of size-based distribution of organotin species on
environmental colloids" Anal. Bioanal. Chem. 390,
1805-1813 (2008).
36 A. Macken et. al. "An
integrated approach to the toxicity assessment of Irish
marine sediments: Validation of established marine
bioassays for the monitoring of Irish marine sediments"
Environ. Int. 34, 1023-1032 (2008).
37. S. Vreysen, A. Maes and H.
Wullaert "Removal of organotin compounds, Cu and Zn from
shipyard wastewaters by adsorption – flocculation: A
technical and economical analysis" Marine Pollution
Bulletin 56, 106-115 (2008).
38. F. Zhao, K. X. Zhao and Y.
N. Wu "Determination of Organotins in Aquatic Food by
Gas Chromatography with Pulsed Flame Photometric
Detection" J. AOAC Int. 91, 653-659-(2008).
Organoarsenical Compound
Analysis with the PFPD
2. D. R. Killelea and J. H.
Aldstadt III, "Solid-phase microextraction method for
gas chromatography with mass spectrometric and pulsed
flame photometric detection: studies of organoarsenical
speciation" J. Chromatog. A. 918, 169-175 (2001).
3. D. R. Killelea, J. H.
Aldstadt III, "Identification of dimethylchloroarsine
near a former herbicide factory by headspace solid-phase
microextraction gas chromatography-mass spectrometry"
Chemosphere, 48, 1003-1008
(2002).
4. A. R. Roerdink and J. H. Aldstadt III, "Sensitive
method for the determination of roxarsone using
solid-phase microextraction with multi-detector gas
chromatography" J. Chromatog. A, 1057, 177–183 (2004).
5. H. Y. Wang, Y. D. Wang, X. F.
Wang and H. M. Hao, "Determination of Lewisite in
ambient air and water by solid phase
microextraction-pulsed flame photometric detector"
Chinese J. Anal. Chem. 33, 1479-1482 (2005).
General
Heteroatom and Additional Analyses with the PFPD
1. H. Jing and A. Amirav,
"Pulsed Flame Photometric Detector - A Step Forward
Towards Universal Heteroatom Selective Detection", J.
Chromatog. A. 805, 177-215 (1998).
2. Aviv Amirav, "The future of
GC detectors in the era of mass spectrometer detection"
AM LAB 33, 28-34 (2001).