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Analysis of chemical warfare agents by gas chromatography-mass spectrometry: Methods for their direct detection and derivatization approaches for the analysis of their degradation products

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Chemical warfare agents (CWAs) are unarguably one of the most feared toxic substances produced by mankind. Their inception in conventional warfare can be traced as far back as the Middle Ages but their full breakthrough as central players in bellic conflicts was not realized until World War I. Since then, more modern CWAs along with efficient methods for their manufacture have emerged and violently shaped the way modern warfare and diplomatic relations are conducted. Owing to their mass destruction ability, counter methods to mitigate their impact appeared almost immediately on par with their development. These efforts have focused on their efficient destruction, development of medical countermeasures and their detection by modern analytical chemistry methods. The following review seeks to provide the reader with a broad introduction on their direct detection by gas chromatography-mass spectrometry (GC-MS) and the various sample derivatization methods available for the analysis of their degradation products. The review concentrates on three of the main CWA classes and includes the nerve agents, the blistering agents and lastly, the incapacitating agents. Each section begins with a brief introduction of the CWA along with discussions of reports dealing with their detection in the intact form by GC-MS. Furthermore, as products arising from their degradation carry as much importance as the agents themselves in the field of forensic analysis, the available derivatization methods of these species are presented for each CWA highlighting some examples from our lab in the Forensic Science Center at the Lawrence Livermore National Laboratory.
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     ProofCheck     
DE GRUYTER      
Carlos A. Valdez1/ Roald N. Leif1/ Saphon Hok1/ Bradley R. Hart1
Analysis of chemical warfare agents by gas
chromatography-mass spectrometry: methods
for their direct detection and derivatization
approaches for the analysis of their degradation
products
            
             
         
Abstract:
Chemical warfare agents (CWAs) are unarguably one of the most feared toxic substances produced by mankind.
Their inception in conventional warfare can be traced as far back as the Middle Ages but their full breakthrough
as central players in bellic conicts was not realized until World War I. Since then, more modern CWAs along
with efficient methods for their manufacture have emerged and violently shaped the way modern warfare and
diplomatic relations are conducted. Owing to their mass destruction ability, counter methods to mitigate their
impact appeared almost immediately on par with their development. These efforts have focused on their effi-
cient destruction, development of medical countermeasures and their detection by modern analyticalchemistry
methods. The following review seeks to provide the reader with a broad introduction on their direct detection
by gas chromatography-mass spectrometry (GC-MS) and the various sample derivatization methods available
for the analysis of their degradation products. The review concentrates on three of the main CWA classes and
includes the nerve agents, the blistering agents and lastly, the incapacitating agents. Each section begins with
a brief introduction of the CWA along with discussions of reports dealing with their detection in the intact
form by GC-MS. Furthermore, as products arising from their degradation carry as much importance as the
agents themselves in the eld of forensic analysis, the available derivatization methods of these species are pre-
sented for each CWA highlighting some examples from our lab in the Forensic Science Center at the Lawrence
Livermore National Laboratory.
Keywords: chemical warfare agents, fentanyl, Lewisite, nerve agents, sulfur mustard
DOI: 10.1515/revac-2017-0007
Received: April 1, 2017; Accepted: May 31, 2017
Introduction
Nowadays, there exists no doubt that chemical warfare agents (CWAs) have radically altered the way modern
warfare is conducted. The worldwide collective fear infused by these toxic substances is undeniably based on
their potential for unparalleled destructive power and mass destruction (Chauhan et al., 2008; Munro, 1994). The
term CWA describes a number of highly toxic chemical compounds that have been used by the military to erad-
icate or fully incapacitate a threat (Ganesan, 2010; Szinicz, 2005). The broad repertoire of toxic compounds that
are designated as Schedule 1 materials by the Organization for the Prohibition of Chemical Weapons (OPCW)
include the fast acting and lethal organophosphorus (OP)-based nerve agents such as sarin (GB, 1), soman
(GD, 2), cyclosarin (GF, 3) belonging to the G-series and (S)-2-(diisopropylamino)ethyl O-ethyl methylphos-
phonothioate (VX, 4) and (S)-2-(diethylamino)ethyl O-isobutyl methylphosphonothioate (VR, 5) belonging to
the V-series (Coughlin & Becker, 2012). In addition, the family of CWAs also includes the blistering agents (vesi-
cants) typied by the mustard gasses such as sulfur mustard (HD, 6) and the nitrogen-based mustards [HN1 (7)
and HN2 (8)]. Similar to the mustards, another commonly employed set of vesicants are the arsenic-containing
Carlos A. Valdez    
      
         
1
     ProofCheck     
   DE GRUYTER
Lewisites such as Lewisite I (9), II (10) and III (11). Lastly, the vast repertoire also contains the incapacitating
agents epitomized by the central nervoussystem-acting agents fentanyl (12) and 3-quinuclidinyl benzilate (BZ,
13) (Figure 1) (Coughlin & Becker, 2012). Although other classes within the CWA space exist such as the choking
and blood agents, these will not be discussed here as excellent reviews covering them are available (Coughlin
& Becker, 2012). In addition, the reader is encouraged to look over the review by Black and Muir (2003), who
describe methods for the detection of CWAs in addition to their degradation products where the subject of
derivatization is discussed in detail.
Figure 1: List of chemical warfare agent classes discussed in this review and their structures.
Detection of CWAs in their intact form has relied on technologies that effectively trap the analyte (e.g. in a
ber) and subsequently analyze it by various analytical means [e.g. a eld deployable gas chromatography-mass
spectrometry (GC-MS) unit] (Hook et al., 2002; Smith et al. 2004; 2005). However, there exist instances where rst
responders to the scene of a presumed agent attack may not nd it in its intact but degraded form. In such cases,
it is necessary to indirectly detect the agent by a systematic analysis of the found by-products. For instance, when
dealing with nerve agents, detection and correct identication of the phosphonic acids produced from their full
hydrolysis is important for chemical forensics reasons (Mayer et al. 2012). Along these lines, prociency tests
(PTs) provided by the OCPW are aimed to recreate real case scenarios involving the employment of CWAs.
During these examinations, degradation products that represent direct markers of these toxic chemicals are
spiked into various matrices (water and soil samples) at concentrations normally lying within the 110 ppm
range. These concentrations are chosen to recreate the levels at which these species may be found in real-case
scenarios. As an example of the impact of the degradation process on these toxic substances consider the nerve
agent GD (2) that degrades initially to its half ester pinacolyl methylphosphonic acid (14) that in turn undergoes
a second hydrolytic step to provide methylphosphonic acid (MPA, 15) and pinacolyl alcohol (PA, 16) (Figure
2A). In a similar fashion and in the case of the sulfur and nitrogen mustards, the analysis of the alcohol by-
products originating from their hydrolysis is a common path to follow when an analysis is undertaken (Figure
2B and C). Thus, if one is faced with a scenario involving oxidative decontamination of HD (6), detection of
thiodiglycol (TDG, 17) and its higher oxidation state thiodiglycol sulfoxide (TDGO, 18) will be a very likely
nding (Figure 2B). With regard to the nitrogen mustards, their degradation will produce largely bis- (for HN1
and HN2) or tris-aminoethyl (for HN3) alcohols as featured in Figure 2C for HN1 (7) leading to the production of
N-ethyldiethanolamine (EDEA, 19). Lastly, if the presence of incapacitating agents is suspected, two divergent
approaches may be taken based on the nature of the members discussed in this class. Thus, when focusing on
the analysis of fentanyls, one is likely to detect these species in their intact form based on their inherent chemical
stability. On the other hand, if the scenario suggests the presence of 3-quinuclinidyl BZ (13), a compound known
for its susceptibility to base-mediated hydrolysis, the analysis will unquestionably include 3-quinuclidinol (3Q,
20) and benzilic acid (BA, 21) (Figure 2D).
2
     ProofCheck     
DE GRUYTER   
Figure 2: Hydrolysis products for selected CWAs and their structures. These products can be used retrospectively as
forensic markers in the identication of the original CWAs.
Among analytical methods that have been developed for CWA analysis along with their degradation prod-
ucts, liquid chromatography-mass spectrometry (LC-MS) and GC-MS unarguably constitute the two most
prominent ones. In the case of LC-MS, the CWA can be directly detected and analyzed along with other analytes
of interest in their intact form. Indeed, LC-MS provides the analytical chemist with a comprehensive glimpse of
the analytes of interest in a mixture along with their degradation product without their prior chemical modica-
tion. However, the practicality of the approach is heavily marginalized for wide employment in the eld mainly
as a result of its yet-to-be-attained portability and high operation cost. On the other hand, GC-MS offers the abil-
ity of rapid sample analysis with minimal preparation, adaptability for deployable systems and a low-cost oper-
ation system making it a ubiquitous benchtop analysis system in most analytical chemistry laboratories. How-
ever, the simplicity experienced with GC-MS comes with drawbacks inherent to the nature of the technique. One
of the most important ones is that GC-MS is virtually blind for species with low to non-existent volatility. For
this reason, derivatization reactions of these species must be performed prior to their analysis in order to chem-
ically convert them into entities with suitable volatility. Among some of the most commonly employed deriva-
tizations in analytical chemistry are silylation, employing N,O-bis(trimethylsilyl)triuoroacetamide (BSTFA)
or N-methyl-N-(trimethylsilyl)triuoroacetamide (MSTFA), alkylation in the form of methylation using dia-
zomethane, trimethylsilyldiazomethane or trimethyloxonium tetrauoroborate (TMO.BF4), and acylation em-
ploying acetic anhydride or other acylating agents. In general, all derivatization reactions employ highly reac-
tive agents that will, for all practical purposes, modify all the analytes (including impurities) in a given mixture,
thus making it vital for the analyst to know beforehand what he/she is searching for. The following review has
been organized in sections dealing with the analysis by GC-MS of the CWAs presented in Figure 1. We begin
by introducing the OP-based nerve agents, followed by the blistering agents and concluding with the incapac-
itating agents. In each section, a brief introduction for each class is given along with published work on their
direct detection by GC-MS. In addition, each CWA class will feature sub-sections that deal with the analysis of
their degradation products and analysis by GC-MS. It is in these sub-sections that we will discuss the various
derivatization methods available to the analyst to make these degradation species suitable for GC-MS studies.
Due to their size and analysis by other means (e.g. UV, uorescence spectroscopy or other detection systems
that do not rely on mass spectral analysis), the blood agents will not be covered in this review.
3
     ProofCheck     
   DE GRUYTER
Nerve agents
Within the CWAs, the most feared members of this realm are the OP-based nerve agents. Though structurally
different (Figure 1), their individual modi operandi share a similar characteristic that involves the inhibition of
the enzyme acetylcholinesterase (AChE) (Friboulet et al., 1990; Shih, Kan & McDonough, 2005). This enzyme is
responsible for breaking down the key neurotransmitter acetylcholine (ACh) thereby restoring the vital process
of muscle contraction/relaxation in the body. Inhibition of AChE results in a buildup of ACh producing a
slowly reversible blockade at synaptic junctions that results in muscle paralysis and eventually death due to
asphyxiation (Bajgar, 2004). The critical step of this inhibitory event is the phosphonylation of AChEs active
site serine residue by the nerve agent (22, Figure 3). Once this modication takes place, the serine cannot act
as an efficient nucleophile in the breakdown of ACh. Treatment of the inhibited enzyme, commonly referred
to as the adducted AChE (23, Figure 3), with highly nucleophilic oxime antidotes results in the breakdown
(i.e. oximolysis) of this adducted serine residue restoring the normal levels of this enzyme. However, if this
adducted intermediate undergoes a partial hydrolysis, becoming what is known as aged AChE (24, Figure 3),
then reactivation cannot be accomplished and results in the demise of the affected individual (Bajgar, 2004).
Figure 3: Proposed mechanism of action for the inhibition of AChE by nerve agents. Normal regeneration of AChE (Path-
way A) can be accomplished after exposure to the agent (Adduction step); however, aging of the adducted enzyme (Path-
way B) is also a possibility leading to a modied serine residue that cannot be regenerated via conventional oxime treat-
ment.
Nerve agents exhibit physical properties that make them suitable candidates for direct detection and analy-
sis by GC-MS means. One such property is their boiling points that fall within the temperature range values for
a typical GC-MS analysis such as GB (158°C), GD (198°C) and GF (239°C) for the G-series, while VX displays
a much higher value while still keeping detectability by GC-MS with a boiling point of 300°C for the V-series
agents. Although polar and to some extent hydrophobic in nature, they do not exhibit the same degree of polar-
ity and hydrophilicity as their main hydrolysis products, namely the phosphonic acids. Thus, it is noteworthy
to mention that it is this quality, in conjunction with the miniaturization of the analytical technique, that has
forged the path for the development of portable GC-MS units. However, in some cases the intact agent will
never be found and it is in these instances that an analysis of its degradation products attains a higher level of
importance. To this end, derivatization reactions primarily in the form of silylation and methylation play a key
role in the retrospective identication of this particularly lethal type of CWAs.
4
     ProofCheck     
DE GRUYTER   
Degradation products as retrospective markers for nerve agent identication
One of the main thrust areas in the global mitigation of nerve agents has focused on technologies to safely and
efficiently destroy them. To this end, several nerve agent decontamination approaches have been explored with
a wide range of results (Ajami & Rebek, 2013; Kim et al., 2011; Yang, Baker & Ward, 1992). One of the earliest
methods includes the use of highly basic, aqueous or alcoholic media (typically with pH values above 12) to
dispose of the agent. These conditions efficiently and rapidly hydrolyze the G-series agents. However, when
dealing with agents belonging to the V-series (e.g. VX) basic conditions result not only in the production of a
non-toxic product (77%) but it also results in the production of EA-2192 (22%) which in itself is as toxic as VX
(Yang et al., 1993; Yang, 1999). The observed product distribution for the basic hydrolysis of VX highlights the
importance for developing a decontamination process that proceeds in a regioselective manner to ultimately
furnish only non-toxic products. Oxidative methods for the destruction of nerve agents have also emerged
and these include the employment of oxidants such as Oxone®(2KHSO5·KHSO4·K2SO4), bleach and peroxides
(e.g. hydrogen peroxide) (Yang et al., 1993). Though these methods result in the degradation of nerve agents
and yield non-toxic by-products, their oxidative nature limits their use when decontamination of expensive
equipment or sensitive materials is needed.
With the variety of methods for the hydrolysis in addition to their natural degradation in the environment,
it is no surprise that methods aimed at the detection of products arising from nerve agents have experienced
an equally important level of attention. Thus, in the sections below we will introduce the various degradation
products arising from nerve agents that serve as key markers for forensic purposes when found in a collected
sample. We have organized the sections with a concise introduction to the species and their nature, and high-
light the derivatization methods that have been applied for their modications and subsequent analysis by
GC-MS. For an excellent and extensive review on analytical methods, by GC-MS and others, for CWA analy-
sis and their degradation products, the reader is encouraged to read the superbly assembled book by Joseph
Caruso (Kroening et al. 2011).
Phosphonic acids
The main degradation products from the hydrolysis (and oxidative hydrolysis) of the OP-based nerve agents are
the phosphonic acid half esters (Compounds 14, 25–28, Figure 4). Further hydrolysis of these esters either under
basic or oxidative conditions leads to a common, ultimate product, namely MPA (15 in Figure 4) (Bizzigotti et al.
2012). Detection of these species in a mixture within the context of CWAs provides a key insight into the nature
of the potential nerve agents present in it and provides testament for their past presence thus yielding important
forensic information. Due to the lack of direct detection of these species by GC-MS means, their initial deriva-
tization using silylation or methylation is a necessary requirement for analysis. In general, by employing the
silylation technique, phosphonic acids have been modied to their tert-butyldimethylsilyl (TBDMS) ethers using
N-(tert-butyldimethylsilyl)-N-methyltriuoroacetamide (MTBSTFA) and to their trimethylsilyl (TMS) ethers
employing BSTFA. Often times, the derivatization of the acids is rapid and efficient as highlighted by the silyla-
tion of the plant hormone regulator ethephon (2-chloroethylphosphonic acid). Ethephon was demonstrated to
undergo a smooth conversion to its bis-tert-butyldimethylsilyl ether when heated at 45°C for 1 h in neat MTB-
STFA. Using this approach, ethephon was detected in water samples, after copious co-evaporation with acetoni-
trile (ACN), in the range of 0.11 ng l1with a reported limit of quantication of 0.1 ng l1(Royer et al., 2006).
Turning our attention to a more relevant report involving phosphonic acids related to CWAs, the same silylat-
ing agent was employed in the efficient derivatization of seven acids related to V- and G-series nerve agents.
These acids included 14,15,25–28 in addition to the sodium salt of ethyl hydrogen dimethylaminophosphate,
the main product from the rst pass hydrolysis of the nerve agent tabun (GA). After determining the optimal
conditions for their silylation (80°C for 45 min in ACN), the method was applied for their detection in water and
soil samples with a reported limit of detection less than 5 pg using GC-ICPMS (Richardson & Caruso, 2007).
Even though silylation is a simple and reliable derivatization technique, there exists room for improvement in
its overall execution and practicality. For example during the silylation protocol, heating is necessary (typically
between 65 and 80°C) for usually 12 h in order to ensure that a low concentration analyte is adequately deriva-
tized. Lastly, the reagent itself is often employed as a reaction medium (i.e. neat) or in excess, thus yielding
a large interfering signal in the GC chromatograph that may obscure other silylated analytes of interest. An
alternative to silylation is methylation employing the universally known reagent, diazomethane. This method
enjoys from two superior attributions relative to silylation, namely the mild conditions at which the derivatiza-
tion takes place (normally ambient temperature) and the absence of interfering by-products in the nal analysis.
However, the drawback in this methodology actually lies in the nature of the reagent itself. Diazomethane is
a highly reactive species that requires its fresh preparation before use if an efficient and high-yielding deriva-
5
     ProofCheck     
   DE GRUYTER
tization is desired. Despite careful storage under an inert atmosphere and refrigeration to extend its lifetime,
it is recommended that after 45 days, a new batch of diazomethane should be prepared (Amphaisri, Palit &
Mallard, 2011; Ghassabian et al., 2012; Harvey & Wahl, 2012). Furthermore, the preparation that at this time
constitutes a recurring endeavor possesses explosive hazards that have pressured the scientic community into
nding other alternatives to conduct methylations such as the use of trimethylsilyldiazomethane (Crenshaw &
Cummings, 2004; Kemsley, 2011).
Figure 4: Degradation pathways of nerve agents leading to the formation of highly diagnostic half phosphonic acid esters
and methylphosphonic acid (15).
To this end, reports involving the methylation of phosphonic acids employing the stable salt TMO.BF4(31,
Figure 5) have started to slowly make a re-appearance in the literature. The use of oxonium salts as alkylating
agents was introduced by the pioneering work of the Meerwein group who described their synthesis and sub-
sequent applications in the alkylation of various functional groups including carboxylic acids (Jo Diem, Burrow
& Fry, 1977; Meerwein et al., 1937). However, it was not until 1998 that these salts experienced use in the realm
of analytical chemistry when they were employed in the derivatization and qualitative detection of various
carboxylic acids present in urine samples (Liebich, Gessele & Woll, 1998). Since then, the use of TMO.BF4as
a methylating agent in the eld of analytical chemistry remained dormant until very recently, when work in
our group demonstrated its use for the effective, efficient and clean methylation of a panel of phosphonic acids
related to nerve agents followed by their unambiguous identication by GC-MS (Valdez, Leif & Alcaraz, 2016)
(Figure 5). Interestingly, this method was applied for their methylation when spiked at a 10 μg g1concentration
in a complex matrix composed of various C16C18 fatty acid methyl esters featured in organic samples during
the 38th OPCW Test that our laboratory participated in. The mechanism for the methylation likely proceeds
via nucleophilic attack of the phosphonic acid oxygen to one of the methyl groups of the trimethyloxonium salt
generating the methylated product, the highly volatile dimethyl ether and tetrauoroboric acid that is conve-
niently removed when neutralization of the mixture is carried out with aqueous sodium bicarbonate (Figure
5).
6
     ProofCheck     
DE GRUYTER   
Figure 5: Proposed mechanism for the methylation of pinacolyl methylphosphonic acid (14) by TMO.BF4(31). The expedi-
ent derivatization yields a methyl ester that is now amenable for detection by GC-MS.
Sulfonic acids
The oxidative degradation of OP-based nerve agents caused by various oxidants such as bleach or hydrogen
peroxide initially results in their hydrolysis by virtue of the water present in the overall process, but also in
the subsequent oxidation of these products. For example, oxidative hydrolysis of the nerve agents VX and
VR initially yields the 2-aminoethanethiol species that when present in an oxidative environment undergo
conversion into their corresponding 2-aminoethylsulfonic acids. Sulfonic acid reactivity toward electrophilic
reagents is expected to be comparable to that of their phosphorus-based counterparts as they both feature low
pKavalues (usually in the vicinity of 23). Two of the most important sulfonic acids arising from nerve agent
oxidative degradation are N,N-diisopropylaminoethyl sulfonic acid (29) and N,N-diethylaminoethyl sulfonic
acid (30) that originate from the agents VX and VR, respectively (vide supra, Figure 4). Their presence in a given
mixture strongly hints at the latent presence of these V-type nerve agents, and due to their crystalline nature
and poor solubility in organic solvents such as methylene chloride or ACN, derivatization of the sulfonic acid
group is mandated in order to carry out a successful GC-MS analysis.
Although methods for GC-MS analysis of sulfonic acids exist, there are a scarce number of reports on the
analysis of 2-aminoethylsulfonic acids. Nevertheless, it is highly expected that the derivatization reactions em-
ployed for the more common, plain sulfonic acids can be similarly applied to 2-aminoethylsulfonic acids. One of
the earliest reports involved sulfonic acids such as taurine and L-cysteic acid that were efficiently silylated with
BSTFA at 110°C for 1 h and subsequently analyzed by GC-MS (Stokke & Helland, 1978). The authors found that
prolonged heating of the reaction mixtures (up to 2 h) involving the taurine and cysteic acids led to the degrada-
tion of the silylated derivatives. Aside from this early report, there exists only one report where silylation has
been used to derivatize sulfonic acid species that are close in structural relationship to 2-aminoethylsulfonic
acids. This report describes the treatment of 2-amino-5-chlorotoluenesulfonic acid and once again L-cysteic
acid but this time employing MSTFA to provide their TBDMS derivatives (Ng & Hupé, 1990). The conditions
for the silylation involve a lower heating temperature (at 70°C) of the sulfonic acids (0.015 mmol) in ACN
and in the presence of an excess mixture of tert-butyldimethylsilyl chloride (0.15 mmol) and MTBSTFA (0.5
mmol) for 24 h. However enough conversion to the silylated derivative had occurred after 1 h for detection
by GC-MS. Therefore, one can expect that in a similar fashion, silylation of 2-aminoethylsulfonic acids asso-
ciated with VX and VR can be accomplished employing MTBSTFA as well as BSTFA as the conditions enjoy
an unparalleled similarity. Indeed it is believed that the analysis of 2-aminoethylsulfonic acids has likely been
performed in a routine basis using silylation as the main derivatization tool, but those results have not made
their appearance in the literature perhaps for their expected simplicity. However, as powerful as silylation may
be as an initial screening reaction for the presence of these species, one must be careful not to rapidly dismiss
their presence if the silylated product is not found. For example, in the 12th OPCW PT, N,N-diethylaminoethyl
sulfonic acid (30) caused major problems to several participating laboratories. Although it was detected easily
in the water sample that underwent the methylation reaction, it was not found in the silylated fractions when
BSTFA and MSTFA were employed. In the end, it was found that 6 out of 19 labs failed to report this chemical
in their report as a result of relying on silylation rather than methylation for this acid (Kuitunen, 2005).
Indeed, methylation has been an additional, reliable way of derivatizing sulfonic acids of this kind for their
subsequent detection and identication by GC-MS. Methylations using diazomethane can be used to efficiently
derivatize these acids as elegantly demonstrated by the Ley group en route to their total synthesis of taurospon-
gin A (Hollowood, Ley & Yamanoi, 2002; Hollowood, Yamanoi & Ley, 2003). Due to the potentially explosive
nature of its preparation and its short shelf life even when stored under an inert atmosphere and at 4°C, other
methylating agents have been developed. As an alternative to diazomethane, our group employed TMO.BF4
(31) in the methylation of N,N-diisopropylaminoethyl sulfonic acid (29) and N,N-diethylaminoethyl sulfonic
7
     ProofCheck     
   DE GRUYTER
acid (30) in methylene chloride to furnish sulfonic acid methyl esters 32 and 33, respectively (Valdez, Leif & Al-
caraz, 2016) (Figure 6). Although none of the components in the reaction, with the exception of the matrix itself
composed of fatty acid methyl esters, were soluble in methylene chloride (TMO.BF4is a salt and the sulfonic
acids are virtually insoluble), the efficient methylation of 29 and 30 was readily accomplished. The methylated
products (32 and 33) of these two important V-series agent markers were detected by GC-MS and veried by the
instruments internal NIST database. A more in-depth discussion on this useful methylating salt can be found
in the section discussing phosphonic acid derivatizations (vide infra). Alternatively, trimethylsilyldiazomethane
can be used as an effective methylating agent, although no reports exist for its use solely in the derivatization
of 29 and 30 for subsequent GC-MS analysis. Nevertheless, trimethylsilyldiazomethane has been used success-
fully in the mild and safer methylation of structurally similar 2-aminosulfonic acid-bearing analogs (Phelam,
Patel & Ellman, 2014).
Figure 6: Methylation of N,N-substituted aminoethyl sulfonic acids using TMO.BF4in methylene chloride. The conversion
to their methyl esters is rapid (<1 h) and at ambient temperature. An important feature of this methodology is the fact
that even if the sulfonic acids are not soluble in DCM, they still undergo the methylation.
Pinacolyl alcohol (3,3-dimethyl-2-butanol)
PA (3,3-dimethyl-2-butanol, 16), in addition to MPA (14), is the other major hydrolysis product of the nerve agent
GD (2). Its presence in a given sample signals the previous or latent presence of this nerve agent in addition to
providing important chemical forensics information. As its importance in this eld is well recognized, PA has
been labeled by OPCW as a Schedule 2 compound. Due to volatility issues, PA is a difficult analyte to detect
by GC-MS means specically when it is present in low concentration (15μl ml1) in mixtures containing
several interfering species. Thus, analytical chemists have relied on its initial derivatization to accomplish the
enhancement of its detection by GC-MS as well as conguring its structure to provide a more volatile product
with different retention time and enhanced sensitivity by GC-MS. Common derivatization reactions on PA have
been based on silylation using BSTFA or MTBSTFA to provide the TMS and the TBDMS derivatives, respectively.
These derivatives possess higher boiling points and feature a more volatile prole relative to that of the native
PA yielding analogs that elute at a later time in the GC column, a quality that becomes convenient if the PA
signal is being obscured by a more abundant interference. As it is common with the use of these derivatization
agents, heating of the mixtures up to 65°C for 23 h is necessary to effect the complete derivatization. This may
create a problem during an OPCW PT when dealing with the derivatization of other analytes in the mixture
that may be temperature sensitive. In addition, in the case of BSTFA, a TMS silyl ether of PA is produced that
is prone to hydrolysis when facing acidic (pH ∼ 4) or basic conditions (pH>11) (Green & Wuts, 2007). In an
attempt of developing a practical and milder methodology that can yield a more stable silylated version of PA,
our laboratory introduced the use of a combination approach using phenyldimethylsilyl chloride (PDMSCl, 34)
and N-methylimidazole (NMI, 35) (Albo et al. 2014). The reaction of PA with PDMSCl in the presence of NMI
generates a silyl ether that features a more extended time in the GC column and is inherently more stable than
its TMS and TBDMS counterparts. The notion behind this approach is the use of the NMI as a nucleophilic
activator of the PDMSCl to generate an intermediate silyl imidazolyl species (36) that is more reactive than the
silyl chloride itself (i.e. in situ activation) (Figure 7). The concept was introduced by the Corey group back in
1972 by using imidazole as a reagent to enhance the tert-butyldimethylsilylation of several alcohols that show
low reactivity for this modication under the most widely used condition (i.e. TBDMSCl and pyridine) (Corey
& Venkateswarlu, 1972). In a more recent report, the Kiessling group introduced NMI as a suitable activator for
uridine monophosphate during their synthesis of uridine diphosphate galactofuranose (Marlow & Kiessling,
2001). Thus, the reaction between PA (16) and this intermediate yields the phenyldimethylsilylated PA (37) and
in the process regenerates the NMI for another round of silyl chloride activation. Even though it may appear
that NMI solely plays the role of a catalytic reactivator in the process, excess of both reagents (PDMSCl and
NMI) is employed to reduce the time for the derivatization and because portions of the NMI are needed to
8
     ProofCheck     
DE GRUYTER   
effectively remove the generated HCl (Figure 7). This approach was used successfullyin the tagging of PA with
the PDMS group in organic sample matrices from the 16th, 32nd and 34th OPCW PTs (Albo et al., 2014). The
derivatization resulted in the production of a PA product that featured a larger retention time and was effective
in increasing the analytes retention time away from the large interfering signals from the complex matrix.
Figure 7: Proposed mechanism for the NMI-mediated phenyldimethylsilylation of PA (16) to furnish PDMS-PA (37). In
this in situ activation of PDMSCl, NMI plays the dual role of (1) enhancing the reactivity of the silyl chloride through acti-
vation and (2) sequestering the generated HCl from the reaction. The efficient silylation of PA using this method occurs in
30 min at ambient temperature.
Blistering agents
Sulfur mustards
The HD class of CWAs can be more accurately described as being composed of a number of different sulfur-
based alkylating agents that share a common mechanism of action. The agship compound within this family
is HD (6), and the proposed mechanism for its alkylation properties is the intermediacy of a highly electrophilic
episulfonium species (38) that arises from an intramolecular SN2 displacement of one of the chlorine atoms by
the sulfur atom (Figure 8). Close contact with these agents causes severe blistering on the skin, and although
these are technically non-lethal agents, complications arising from their incapacitating power can lead to death
if not treated properly. Decontamination technologies for these species involve the use of basic formulations
that result in the hydrolysis of the agent and the production of TDG (17) that, in turn, is no longer a vesicant
and non-toxic in nature (Bizzigotti et al., 2012). Oxidative decontamination has also found application with
these types of agents; thus treatment of HD with oxidants (e.g. bleach) leads to the formation of its sulfoxide
(TDGO, 18) and sulfone (thiodiglycol sulfone, 39) by-products. Although sulfoxides are viable intermediates
during the oxidative process, their detection might be hampered by the fact that under the highly oxidative
conditions (i.e. excess oxidant), they are further converted to their corresponding sulfone products (Figure 8).
For this reason sulfoxides such as TDGO (18) are normally encountered during the analysis of urine and plasma
samples obtained from mustard gas-affected individuals as they form a large part of the species arising from
mustard gas metabolism. TDG and TDGO may be analyzed by LC-MS methods; however, it is the low levels of
detection encountered with this approach (typically 10 ng ml1) that severely hamper it from wide usage when
tackling these analytes. Interestingly, detection of intact TDG and TDGO can be accomplished using GC-MS;
9
     ProofCheck     
   DE GRUYTER
however, broadening of the peaks is typical for these kinds of compounds, thus making their derivatizations a
necessary step in their analysis. The following section will focus on the most commonly employed HD (6) and
its degradation products.
Figure 8: Mode of alkylation by the sulfur mustards (shown for HD) and their main degradation products from their ox-
idative hydrolysis.
Thiodiglycol
The main product arising from the complete, basic hydrolysis of HD is TDG (17) (Figure 8). Detection of TDG
by GC-MS requires its prior derivatization as demonstrated by its detection in water, serum and urine after
its conversion with MTBSTFA (43) to bis-tert-butyldimethylsilylated TDG (44) (Figure 9A). Ohsawa et al. (2004)
reported a 55% recovery of the derivatized material for the method that also featured an impressive limit of
detection (LOD) of 5.4 ng ml1for the water sample. The method involves the treatment of TDG with MTBSTFA
(with 1% TBDMSCl) in the form of a co-solvent with ACN (1:1) followed by heating at 60°C for 1 h. The reported
LOD for the two remaining matrices, serum and urine, were found to be 7 and 100 ng ml1, respectively, thus
making it a viable method for the analysis of this HD product in aqueous samples. As briey noted earlier,
the use of uorinated tags aids increases the sensitivity for detecting the analyte due to the electron-capturing
ability of the uorine atom (vide supra). Thus, it is not surprising that derivatization methods that introduce
these powerful chemical reporters into TDG have been developed. Thus, in an early report derivatization of
TDG with heptauorobutyl anhydride (HFBA, 45) to provide the bis-heptauorobutyl derivative (46) was de-
scribed. The method was successfully applied to the derivatization of TDG present in rat urine samples after
water removal and reaction with HFBA in dry ethyl acetate, in the presence of 5 Å molecular sieves to further
scavenge any residual water,and heating the mixture to 60°C for 1 h (Jakubowski et al., 1990) (Figure 9B). After
the derivatization was completed, the sample was dried, re-suspended in ethyl acetate and immediately ana-
lyzed by EI-GC-MS using selected ion monitoring (SIM). In another early report, extremely low LOD values
(down to 1 ng ml1, 1 ppb) in urine samples were disclosed by reacting TDG with pentauorobenzoyl chloride
(PFBC, 47) in pyridine at ambient temperature for 5 min to furnish uorinated TDG derivative 48 followed by
analysis using negative ion chemical ionization GC-MS (Black & Read, 1988) (Figure 9C). In yet another example
involving uorine tag introduction into TDG, Popiel et al. (2014) employed triuoroacetyl imidazole (TFAI, 49)
to convert it to bis-triuoroacetylated TDG (50). The reaction was carried out in methylene chloride under mild
conditions (1 h at 30°C). Using this methodology, the authors reported the LOD value down to 0.01 ng ml1,
which when compared to additional studies described in their paper is two orders of magnitude better than
the one obtained when silylation (with BSTFA) is employed (Popiel et al., 2014) (Figure 9D). As an additional
note, the chemistry group from Vertox laboratories performed a set of designed to compare the reactivity of
three different triuoroacetylating agents including TFAI to produce 50. The three agents were TFAI (49), triu-
oroacetylbenzotriazole (TFABT, 51) and their then newly developed triuoroacetylbenzimidazole (TFABI, 52)
(Pardasani et al. 2004) (Figure 9E). During their work, TFAI and TFABI were found to be superior triuoroacety-
lating agents than TFABT when running the derivatization of TDG and other homologous thio-containing alco-
hols closely related to the HD. Their explanation for the observed reactivity was the lower pKavalue exhibited
by the imidazole and benzimidazole moieties in 49 and 52 (7.0) relative to the one exhibited by the triazole
heterocycle in 51 (8.3). The reaction was found to proceed smoothly at ambient temperature and just 5 min,
with little product yield improvement after extending the reaction time (Figure 9E).
10
     ProofCheck     
DE GRUYTER   
Figure 9: Derivatization of TDG employing BSTFA (A) and various uorine-containing derivatization agents (BE).
Thiodiglycol sulfoxide
Another by-product arising from the oxidative hydrolysis of HD, and also as a result of its metabolism in hu-
mans, is TDGO (18). Due to the similarity not only in structure but reactivity as wellto TDG, it is not surprising
to see that TDGO has been the subject of the same set of derivatizations for GC-MS analysis. However, the reac-
tivity of the hydroxyl groups in TDGO is expected to be higher than that of the ones present in TDG based on
inductive effects originating from the sulfoxide moiety. Due to the observed poor LOD values obtained when
silylation is used as a derivatization means for TDGO, uorinated tags have been more benecial when their la-
beling and subsequent detection by GC-MS is needed. Thus, in showcasing one application of this kind, HFBA
(45) used to convert TDGO into bis-heptauorobutyrylated TDGO (53) was used and analyzed in urine samples
using isotope dilution GC-MS-MS (Boyer et al. 2004). The derivatization involved the treatment of the sample,
after complete water removal, with HFBA in ACN at 50°C for merely 30 min. Four years later, the Black group
developed a method for TDGO detection in urine samples this time via its reaction with heptauorobutyl im-
idazole (HFBI, 54). In this report, the protocol involves the heating of the dried sample containing the TDGO
(as well as TDG) in ACN in the presence of HFBI at 50°C for only 30 min to furnish 53. Subsequent detection
of the uorinated TDGO was accomplished using isotope dilution GC-ion trap tandem mass spectrometry, re-
porting levels of TDG (obtained from the reduction of TDGO by titanium chloride in the urine sample) down
to 104 ng ml1(Riches, Read & Black, 2007) (Figure 10). During their analysis of TDG, the Popiel and Vanni-
nen groups found that the reaction of TDGO employing TFAI (49) worked exceptionally well in converting it
into its bis-triuoroacetylated analog (55). The reaction was found to proceed in a number of organic solvents
(including dichloromethane and ACN) and resulted in the rapid conversion (1 min at 30°C) of TDGO to 55
(Popiel et al., 2014). It is noteworthy to mention that for the specic GC-MS analysis of sulfoxide species such
as TDGO, triuoroacetylation using agents that produce acid by-product (such as triuoroacetic anhydride or
triuoroacetyl chloride) result in the inefficient derivatization of the parent compound. The reason for the re-
duced derivatization efficiency is that sulfoxide species tend to undergo Pummerer-type rearrangements in the
11
     ProofCheck     
   DE GRUYTER
presence of the generated acid (i.e. triuoroacetic acid), a pathway that is highly unlikely when the imidazole-
based triuoroacetylating agents such as TFAI are employed.
Figure 10: Derivatization of TDGO (18) with uorine-bearing tags for its analysis by GC-MS.
Nitrogen mustards
Just as the HD family, the nitrogen mustards are powerful vesicants. They are powerful alkylating agents that
cause severe DNA damage by acting as non-specic crosslinking agents. Their mode of action is very similar to
the one displayed by the HD, which involves the sequential displacement (SN2-like) of their chlorine atoms via
the intermediacy of an aziridinium ion. This intermediate displays highly electrophilic character and as such
reacts with a large range of nucleophiles. Decontamination approaches aimed at nitrogen mustards have been
similar to the ones undertaken for the HD and most CWAs, namely basic and oxidative hydrolysis. Degradation
of the nitrogen mustards leads to their alcohol-containing products known as ethanolamines or 2-aminoethyl
alcohols (Figure 11). GC-MS detection and analysis of these species in their intact form is possible; however,
these have received less attention than the HD. Their ease of detection is a direct result of their volatility and
GC equipped with specic nitrogen detectors that can provide accurate and sensitive readouts for the intact
agents. Interestingly, as a result of their high reactivity towards various nucleophiles including water, it is their
degradation products arising from hydrolysis (basic or oxidative) that have received the bulk of the attention
as these are the most likely encountered species in a real-case scenario involving their use.
12
     ProofCheck     
DE GRUYTER   
Figure 11: 2-Aminoethyl alcohol-containing products arising from the hydrolysis of the nitrogen mustards and the oxida-
tive or basic hydrolysis of the V-series agents and the undertaken silylation strategies used for their analysis by GC-MS.
Ethanolamines (2-aminoethyl alcohols)
Of the various degradation products arising from the hydrolysis of the nitrogen mustards (HN1 (7), HN2 (8) and
HN3 (56)), the ones bearing the 2-aminoethyl alcohol functionality stand out as the most prominent ones. The
2-aminoethyl alcohols arising from the hydrolysis of the nitrogen mustards HN1, HN2 and HN3 are EDEA (57),
N-methyldiethanolamine (MDEA, 19) and triethanolamine (58), respectively (Figure 11). Also as importantly,
the 2-aminoethyl alcohol functionality can be found to be present in the products originating from the complete
hydrolysis of VX (4) and VR (5), namely N,N-diisopropylaminoethyl alcohol (59) and N,N-diethylaminoethyl
alcohol (60) (Figure 11). Consequently, after realization of this link between these products to the aforemen-
tioned CWAs, it becomes clear why detecting these species in a given sample remains an important task in the
overall study of these toxic species.
Detection of these hydrolysis products by GC-MS means is well reported and in these cases the initial deriva-
tization of these analytes, for example via silylation, is needed. For example, MTBSTFA was used to silylate
alcohols 19,57 and 58 present in water, urine and blood samples with the reported LOD for the three alcohols
in the water sample found to be at 2.5, 2.5 and 10 ng ml1, respectively (Ohsawa & Seto, 2006). The silylation
reaction involved the complete drying of the aqueous mixture followed by the heating of the residue to 60°C for
1 h in the presence of excess MTBSTFA. The sample recovery for the watersamples were found to be the highest
at 88%, 88% and 79% for 57,19 and 58, respectively, followed by recoveries in urine in the range of 72%100%
and recoveries from serum lying in the low 7%31% for all three alcohols (Ohsawa & Seto, 2006). It is important
to note that Ohsawa and Seto suggest that the addition of HCl to the aqueous mixture prior to evaporation to
dryness increases the recovery of the alcohols during the derivatization step. This same acidic treatment was
subsequently employed by the Alp group when derivatizing EDEA (19) and MDEA (57), using BSTFA, for their
GC-MS analysis in rat urine samples with reported LOD values of 2.5 ng ml1for EDEA and 1.6 ng ml1for
MDEA (Kenar & Alp, 2011). Similarly, heating of the alcohols in the presence of BSTFA in ACN was conducted
at 60°C for 30 min to carry out their derivatization. As an alternate procedure to the well-established silylat-
ing methods mentioned above, our laboratory found that derivatization of several 2-aminoethyl alcohols with
the phenyldimethylsilyl moiety can be accomplished under mild conditions with the in situ activation method
employing phenyldimethylchlorosilane and NMI. The efficient silylation of a panel of 2-aminoethyl alcohols in-
cluding the ones linked to the nitrogen mustards (19,57,58) was demonstrated. In addition, the same approach
was utilized in the efficient derivatization of alcohols 59 and 60 that are the oxidative hydrolysis products of VX
and VR, respectively, to furnish silylated products 61 and 62. The work demonstrated the advantage of using
NMI over pyridine as a powerful nucleophilic base to activate the PDMSCl (Valdez, Leif & Hart, 2014a). The
protocol involves the same conditions (ambient temperature and 30 min) as the one described in earlier work
from our laboratory involving the silylation of PA (vide supra, Figure 7).
Methylation as a measure of formulating suitable derivatives of 2-aminoethyl alcohols for GC-MS analysis
has not been a widespread practice. As diazomethane is the most employed reagent for the introduction of
the methyl moiety into analytes, it is its high degree of electrophilicity that inherently works against it when
dealing with this class of substrates. Diazomethane is used in large excess leading to the derivatization of not
only the hydroxyl groups but also the highly nucleophilic tertiary nitrogen center that ultimately converts the
molecule into a quaternary salt thus severely handicapping its volatility and subsequent detection by GC-MS.
Methylation of amino alcohols exists but these are conducted strongly under basic conditions (e.g. sodium
hydride and methyl iodide), thus assuring that the hydroxyl groups are the most nucleophilic centers in the
molecule even over other amine groups (Corda et al., 1994; Cacciapaglia et al., 2005).
Lewisites
Lewisites are arsenic-based CWAs that like nitrogen/HD also belong to the blistering agent class. The most
common members of this class are Lewisite I (9), II (10) and III (11), all featuring an arsenic (III) center cova-
lently bonded to at least one sp2carbon atom of the 2-chlorovinyl group (Figure 1). In the case of Lewisite III
(11), all three substituents on the arsenic are 2-chlorovinyl units. Interestingly, the term Lewisite is commonly
used to describe the organoarsenical mixture that results when arsenic trichloride reacts with acetylene gas in
the presence of metal chloride catalysts such as aluminum chloride, mercury (II) chloride, antimony (III) chlo-
ride, or the combination of these in aqueous HCl media (Jarman, 1959; Jones, Rosser & Woodward, 1949a; Jones,
Vallender & Woodward, 1949b). Thus, despite the use of several rounds of fractional distillations for purica-
tion, the composition of munition-grade Lewisites as well as Lewisite standards synthesized in a laboratory
13
     ProofCheck     
   DE GRUYTER
generally consists of 90% Lewisite I, 9% Lewisite II, and <1% Lewisite III. Direct detection of Lewisites in
the intact form by GC-MS is extremely difficult due to the instability of these compounds under conditions
where minimal moisture exists. Furthermore, the presence of alcohols, or for that matter thiols which possess
an unmatched affinity for their arsenic center, may react to form unwanted adducts in the instrument aided
by the heat of the GC port. Lastly, their detection in the intact form is further complicated by the deterioration
of the GC stationary phases due to the acidity and corrosiveness of the samples themselves that is a direct
consequence of their high sensitivity to moisture. This represents a major problem leading to the inability to
achieve linear responses during their analysis resulting in the irreproducible quantitation of the intact species
particularly when these are present in low concentrations. Interestingly, Lewisite III (11) is a non-vesicant, as
its arsenic center is non-electrophilic and unreactive to O- and S-nucleophiles and stable to hydrolysis in aque-
ous media, which is the reason why it can be directly analyzed by GC-MS without derivatization. At higher
concentrations, Lewisites I and II can also be analyzed by GC-MS without the need for derivatizations (Black
& Muir, 2003; Epure, Grigoriu & Filipescu, 2010).
Arsonous, arsinic acids and their oxides
Lewisite I (9) rapidly hydrolyzes to 2-chlorovinylarsonous acid (CVAA, 63) which exists in an equilibrium with
2-chlorovinylarsonous oxide (CVAO, 64). In a separate reaction path, CVAO (65) can further oxidize into 2-
chlorovinylarsonic acid (CVAOA, 65). Due to their polar and non-volatile nature, compounds 63 and 64 require
derivatization prior to their analysis by GC-MS. In contrast, their counterpart exhibiting a higher order of oxi-
dation (e.g. 65) can be directly detected by LC-MS only and no reports exist regarding their analysis by GC-MS.
Similarly, Lewisite II (10) is known to rapidly hydrolyze to bis-(2-chlorovinyl)chloroarsinic acid (BCVAA, 66)
which further participates in the degradation process via a condensation reaction to produce arsenic dimer
67 (Popiel & Sankowska, 2011) (Figure 12). As in the case of Lewisite I, BCVAA (66) can further oxidize to 2-
chlorovinylarsonic acid (BCVAOA, 69). As noted above for Lewisite I, BCVAA (66) can be detected by GC-MS
after derivatization, while its oxidation product (BCVAOA, 68) can be directly detected by LC-MS means.
14
     ProofCheck     
DE GRUYTER   
Figure 12: Hydrolysis pathways for the vesicants Lewisite I (9) and Lewisite II (10).
Derivatization of Lewisite I (9) and its degradation products CVAA (63) and CVAO (64) is commonly
done using thiol-based reagents that lead to the formation of the general 2-chlorovinylarsine thioether prod-
ucts with formulas 69 and 70. These products can be acyclic or cyclic in nature depending on what kind
of thiol is used; thus if a monothiol regent is used, a derivatized product with the structure of 69 will be
obtained, while if a dithiol reagent is used, a derivatized product like 70 will be formed. Derivatization of
Lewisite II (10) and its hydrolysis product BCVAA (66) with various thiols (monothiols or dithiols) leads to
their respective thioether derivatization products. Thus, monothiol and dithiol reagents such as ethanethiol,
propanethiol, butanethiol, 3,4-dimercaptotoluene, 2,3-dimercaptopropanol, thioglycolic acid methyl and ethyl
ester, 1,2-ethanedithiol (EDT) (Fowler, Steward & Weinberg, 1991; Stankov et al., 2011), 1,3-propanedithiol
(PDT) (Tomkins, Sega & Ho, 2001; Wooten, Ashley & Calafat, 2002) and 1,4-butanedithiol (BDT) have been
successfully utilized as derivatization reagents for Lewisite analysis.
In one key report, the derivatization of Lewisites I and II in hydrocarbon matrices employing a series of
aliphatic thiols ranging from ethanethiol to dodecanethiol was carried out and analysis of the resulting sam-
ples was performed using GC-MS-SIM. Bis-derivatives of Lewisite I were prepared up to the C8-thiol homolog,
while those of Lewisite II included up to their C12 aliphatic thiols (Muir et al., 2004). Propanethiol, butanethiol
and pentanethiol were found to be superior to their higher thiol counterparts as derivatization agents result-
ing in superb LOD values reported at <1 μg ml1. In another report from the same laboratory, the authors
used a statistical experimental design and developed a thermal desorption with the TD-GC-MS-SIM technique
optimized for the detection of Lewisites IIII in headspace/air samples in ultra-trace quantities. Desorption
tubes were spiked with butanethiol (71) or 3,4-mercaptotoluene (72) and were then reacted with methanol so-
lutions of the Lewisites followed by thermal desorption and analysis by TD-GC-MS-SIM (Muir et al., 2005).
Butanethiol derivatives of Lewisites I (73) and II (74) were achieved with LODs of 30 μg m3in air samples
for each. Interestingly, when 72 was employed for the derivatization of Lewisite II, the same product (75) aris-
ing from Lewisite I was also observed, suggesting a loss of chlorovinyl upon nucleophilic attack of the second
sulfur atom (Figure 13A and B). The result was explained by citing the greater stability that is accomplished by
forming two string As-S bonds and a highly stable ve-membered ring structure (Muir et al., 2005). Thus, the
authors add the cautionary note that employment of 3,4-dimercaptotoluene (72) can lead to an over-estimation
of the quantity of Lewisite I and an under-estimation of Lewisite II, offering the use of butanethiol (71) instead.
Another method for the derivatization of Lewisites involves the use of dispersive derivatization liquid-liquid
microextraction-GC-MS in scanning and SIM modes. In this report, detection of the dithiol [EDT, PDT, BDT, and
1,5-pentanedithiol derivatives of CVAA (63)] was described. The results indicate that CVAA can be directly and
selectively derivatized in diluted urine samples employing these dithiols (Naseri et al., 2014). The method was
shown to be reproducible, selective and sensitive for the EDT derivative (76) of CVAA and suitable for verifying
human exposure to Lewisite by the analysis of CVAA as the main metabolic biomarker, with an impressive LOD
of 0.015 μg l1(Figure 13C). Interestingly, the nature of the solvent mixture employed bears importance as the
methanols purpose was its use as a dispersive agent, while the chloroform and EDT served as the extraction
solvent and derivatization agent, respectively.
15
     ProofCheck     
   DE GRUYTER
Figure 13: Derivatization of Lewisites I and II using thiol-based reagents.
Based on the aforementioned examples, one can see that thiols have certainly been the leading species as far
as derivatization agents are concerned for the analysis of Lewisites and their degradation products. However,
few reports exist where alcohols have appeared as viable entities for their derivatization. In one instance, TDG
(77) has been successfully employed as an alcohol-based derivatization agent for Lewisites I (9) and II (10)
(Figure 14A). Both instances involved the heating to 40°C of the Lewisites in the presence of 77 in water. The
approach was tested in a water matrix featured in an OPCW PT and its main highlight was the fact that the
derivatization can be carried out in water, thus abolishing the need for the more traditional two-step process
involving drying followed by BSTFA derivatization. In the case of Lewisite I, the product that results from
its reaction with 77 is the eight-membered ring adduct 78 which was detected by GC-MS means down to a
concentration of 10 ppb (Figure 14A). Similarly, Lewisite II was reacted under the same conditions with 77 to
provide the bis-substituted TDG adduct 79. The method was used to detect the presence of Lewisite II down
to only 100 ppm levels of concentration demonstrating its much reduced performance when compared to the
derivatization and detection of Lewisite I (Figure 14A) (Sokolowski & Konopski, 2008; Sokolowski, Konopski &
Froebe, 2008). Lastly, as a nal note on the use of alcohols and the potential they hold as derivatizing species for
the modication of Lewisites, a report describing a thorough assessment of alcohol reactivity toward Lewisite I
exists wherein a range of aliphatic alcohols was studied in order to see if any stability could be conferred to the
dialkyl arsonite products for GC-MS analysis. It was found that all the examined alcohols rapidly reacted with
Lewisite I (spiked in soil samples) but only those bearing carbon chain lengths of C5, C6and C8yielded dialkyl
arsonite adducts (80–82) stable enough for observation by GC-MS (Epure, Grigoriu & Filipescu, 2010) (Figure
14B). Although no quantitative studies were reported when employing these alcohols, the method represents
an alternative approach to the use of thiols for the study of this type of CWA. Thus, it is an undeniable fact
that these studies demonstrate that there is much to be discovered in the chemical space that is available to the
analytical chemist from the alcohol family.
16
     ProofCheck     
DE GRUYTER   
Figure 14: Use of alcohol-based derivatization agents for Lewisites I and II.
Incapacitating agents
Fentanyls
Within the class of incapacitating agents, one of the most notorious members that have recently gained wide
attention is the fentanyls. Some of these synthetic opioids display potencies that are far beyond the one exhibited
by the most famous painkiller used in the clinical setting, namely morphine. For example, fentanyl (12), the
agship compound in this family exhibits potency of 100 times that of morphine (Figure 15). As expected
other, more powerful analogs of this compound have been synthesized since Janssens landmark synthesis of
12, such as remifentanil (83), carfentanil (84) and sufentanil (85) with demonstrated potencies ranging from
200× to 1000× more than that exhibited by morphine.
Figure 15: Selected members of the fentanyl class of synthetic opioids. The bracketed numbers represent their individual
potencies relative to morphine.
These compounds act by binding transmembrane μ-opioid receptors on cell surfaces activating a cascade
of intracellular signals that lead to their biological effect (Grass 1992a; 1992b; 2000). Commonly employed as
potent analgesics during perioperative procedures in a clinical setting, they have emerged as the main choice
for physicians when a patient is undergoing complex surgical procedure in addition to becoming key players
17
     ProofCheck     
   DE GRUYTER
in the management of pain for patients with cancer (Friedrichsdorf & Postier, 2014; Lee et al., 2014). Their
rapid and effective biological action on the nervous system is the main reason for their use as incapacitating
agents by the armed forces. A notable example of this use was the employment of two powerful members of
this class in the aerosolized form, remifentanil (83) and carfentanil (84), to subdue Chechen terrorists during
the Moscow Theater crisis in 2002 leading to 170 fatalities that included civilians (Coupland, 2003; Riches et al.,
2012; Rieder et al., 2003; Wax, Becker & Curry, 2003). In addition, very recently their military use has transitioned
into their illicit distribution in society resulting in numerous fatalities (Breindahl et al., 2017; Katselou et al.,
2016; Rojkiewicz et al., 2016). Aside from their powerful neurological effects, a more concerning fact over these
class of drugs by various agencies including the Drug Enforcement Agency is the efficient, straightforward and
large-scale adaptability of their synthetic routes (Gupta et al., 2005; Valdez, Leif & Mayer, 2014b). Consequently,
medical countermeasure approaches to alleviate their biological impact due to an overdose in an individual is
one of the main branches aimed at starting a program to effect their capture and neutralization (Mayer et al.,
2016). Due to their stability and resistance toward acid- or base-mediated hydrolysis (Garg et al., 2010), detection
in their intact form is usually encountered. As a result of this, LC-MS has been the leading technique for their
analysis and quantication greatly aided by fentanyls innate ultraviolet absorption and its aqueous solubility
when converted to their hydrochloride or citrate salts (as commonly employed in the medical eld) (Almoussa
et al., 2011; Cooreman et al., 2010; Wang & Bernert, 2006).
In the realm of GC-MS, fentanyls themselves have not been a reason for method development; however,
few reports exist where the free base can be directly detected and quantied using synthesized standards
and deuterated analogs (Gardner et al., 2015; Kudo et al., 2013; Ohta, Suzuki & Ogasawara, 1999; Van Nim-
men & Veulemans, 2007). Interestingly, GC-MS has played a key role in the analysis of products arising from
their metabolism as elegantly demonstrated by the analysis of the major metabolite arising from the action
of esterases on remifentanil (83). It is known that hydrolysis of the distal, primary ester occurs more read-
ily than the more congested tertiary methyl ester in 83 to yield carboxylic acid-containing intermediate 86.
Acid 86 was effectively silylated with BSTFA in conjunction with TMS chloride at 70°C for merely 30 min to
provide silylated acid 87 that was detectable by GC-MS (Lehner et al., 2000) (Figure 16A). In a similar fash-
ion, the N-dealkylated metabolic products referred to as nor-fentanyls have been analyzed after their adequate
derivatization. In this specic scenario, metabolic dealkylation of sufentanil (85) and alfentanil (88) produces
the piperidine-containing metabolite (89) that coincidentally is the same intermediate for both metabolic pro-
cesses. Treatment of 89 with PFBC (47) furnishes the pentauorobenzamide product (90) that showed enhanced
detectability by GC-MS by virtue of the electron-capturing ability of the uorinated tag (Valaer et al., 1997)
(Figure 16B). This method allowed for the detection of the dealkylated metabolites of fentanyl, sufentanil and
alfentanil as low as 0.3 ng ml1in urine samples. As an alternate route to the analysis of nor-fentanyl (91),
derivatization employing pentauoropropionyl anhydride (92) yielded the pentauoroamide product 93 that
was easily detected by GC-MS (Figure 16C). The developed methodology allowed reported LODs of 0.08 ng
ml1for nor-fentanyl as well as nor-alfentanil 89 in urine samples (Strano-Rosi et al., 2011).
18
     ProofCheck     
DE GRUYTER   
Figure 16: Derivatization of products arising from the hydrolytic and/or metabolic breakdown of various fentanyl-related
compounds. The use of uorinated derivatization tags greatly enhances the detection of these species due to the unsur-
passed electron-capture abilities of the uorine atoms.
3-Quinuclidinyl benzilate
3-Quinuclidinyl benzilate, also known by its IUPAC name 1-azabicyclo[2.2.2]oct-3-yl 2-
hydroxy-2,2-diphenylacetate (13), is an anticholinergic agent that affects both the peripheral and central
nervous systems (Fusek et al. 2009). This chemical is commonly referred to by the NATO code BZ, although
another common acronym is QNB, and is the only incapacitating agent classied as a Schedule 2 compound
by the OPCW (Szinicz, 2005). The activity of BZ arises from its competitive inhibition of muscarinic receptors
(Eglen, 2006), blocking ACh binding resulting in anticholinergic delirium, cognitive dysfunction, hallucina-
tions and inability to function. BZ has been used as an incapacitating agent by the military for the reasons cited
above and its dissemination in the aerosol form has been deemed effective as its primary route of absorption
is through the respiratory system (Misik, 2013).
BZ can be analyzed directly by GC-MS without any prior treatment (Byrd et al., 1992; Byrd, Sniegoski &
White, 1988; Kostianinen, 2000). Derivatization techniques such as silylation and methylation aimed selectively
at the hydroxyl group of 13 are not known. There are two reasons that account for this behavior; the rst one
is the fact that the hydroxyl group is highly hindered (tertiary alcohol) and the second is the greater nucle-
ophilicity and accessibility of the quinuclidine nitrogen. It is this nitrogen that often nds itself at the epicenter
of reactions involving electrophilic reagents such as methyl iodide (94), for example, to generate the BZ-Me
salts (95) that are more suitable for LC-MS analysis (Dolle et al., 2001) (Figure 17). Furthermore, the presence
of the ester moiety joining the two halves of BZ additionally complicates matters as basic conditions usually
employed to enhance the nucleophilicity of hydroxyl groups over nitrogen centers often result in the cleavage
of this bond. For these reasons, and the fact that BZ is amenable for UV detection, LC-MS has been a better
technique to carry out its analysis (Black & Read, 2005).
19
     ProofCheck     
   DE GRUYTER
Figure 17: Methylation of BZ resulting in the modication of the nitrogen center to generate BZ-Me salt (95) suitable for
LC-MS applications.
Benzilic acid
BA is one of the two products arising from the breakdown of BZ (Byrd et al., 1992; Hull, Rosenblatt & Ep-
stein, 1979; Sniegoski, Byrd & White, 1989). BA (21) exhibits poor gas chromatographic behavior, especially on
common nonpolar general purpose column phases, such as the 5% phenyl-methylpolysiloxane column phase,
and therefore derivatization is a necessity for its detection by GC-MS means. MTBSTFA has been a convenient
derivatizing agent for BA and readily forms the bis-(tert-butyldimethylsilyl) BA (96) (Figure 18). The conditions
used for this transformation involves heating of the mixture at 60°C for 30 min in a 1:1 chloroform:MTBSTFA
mixture (Park et al., 2013). In this work, the authors report LOD values in the range of 0.080.01 ng ml1for BA
along with other CWA degradation products when spiked in water samples. Conrmation of the efficiency of
the reaction, reached after several optimization studies on the method, was validated by using the protocol on
the detection of BA in OPCW test samples. Methylation of BA has seldom found use as an alternative derivatiza-
tion protocol but has employed diazomethane. The methylation involves the reaction of BA with diazomethane
in acetone and yields the bis-methylated adduct (97) which possesses suitable volatility for GC-MS (Amphaisri,
Palit & Mallard, 2011) (Figure 18). In their report, Amphaisri et al. also show their studies on the methylating
power of two commercially available agents, namely, trimethylphenylammonium hydroxide (98) and trimethyl-
sulfonium hydroxide (99). It was found that both of these reagents performed equally well but still below the
more established diazomethane reagent despite their added benet of their non-explosive nature. Thus, the
thermally assisted methylations using these two reagents yielded signicantly noisier chromatograms relative
to their diazomethane counterpart; however, detection of BA and phosphonic acids related to CWAs was ac-
complished down to levels of 0.5 μg ml1. In addition to diazomethane, we found that in our hands the use of
TMO.BF4also works efficiently at providing the bis-methylated adduct 97 during the 40th OPCW PT that we
participated in. The methylation under our conditions works at ambient temperature and for 2 h (Figure 18).
Figure 18: Silylation and methylation strategies for benzilic acid for GC-MS analysis.
20
     ProofCheck     
DE GRUYTER   
3-Quinuclidinol
3Q (20) is a bicyclic amino alcohol that is a key indicator for the presence of BZ due to its strong structural
connection with this incapacitating agent. The alcohol in the underivatized form is not t for direct GC-MS
detection as its volatility prole is not appropriate in addition to the broadness of the peak that usually hinders
detection even further. Derivatization certainly has provided great aid in the overall detection of 3Q by GC-
MS means with silylation and carbamate generation presenting themselves as two most successful approaches.
Unfortunately, and as alluded to earlier when BZ and BA were discussed, not many reports exist for its deriva-
tization. One of the reasons for this apparent lack of reports is the fact that in this molecule, in addition to the
alcohol functionality, there exists the nucleophilic tertiary nitrogen that possesses high affinity for electrophilic
reagents such as BSTFA and diazomethane. Thus, it is often this high level of reactivity that is exploited when
the sole modication of the hydroxyl group is required. This has been accomplished by temporarily blocking
the amine using boron trihydride (100) resulting in the formation of amino-borane complex 101 (Figure 19).
Complexes such as 101 are highly stable and labile only in the presence of acid (e.g. HCl), thus permitting the
modication of the hydroxyl group, in this instance via methylation using sodium hydride and methyl iodide.
Once the methylation of the hydroxyl moiety has been done, hydrolysis of the amino-borane complex using
HCl furnishes the O-methylated 3Q product 102 in good yields (Stotter et al., 1987) (Figure 19). In the realm of
silylations, MTBSTFA and BSTFA have found application for derivatizing 3Q involving a hollow ber-protected
liquid phase microextraction (HF-LPME) procedure that involved the in situ derivatization of the analyte when
present in water. The hollow ber served as a hydrophobic protective barrier from water to the derivatizing
agent while the extraction/derivatization was underway. It was found that extraction of the aqueous matrix
with a 1:1 chloroform:MTBSTFA followed by additional exposure of the ber to MTBSTFA gave the highest
uptake of 3Q in the protocol via its conversion to 3Q-TBDMS (103) (Lee et al., 2008) (Figure 19). Interestingly, it
was found that the use of a 1:1 chloroform:BSTFA did not provide better uptake of 3Q relative to its MTBSTFA
counterpart (i.e., conversion to 3Q-TMS 104), but it was a superior choice in the analysis of other aminoethyl al-
cohols. The authors report LOD of the various CWA degradation products for the HF-LPME procedure ranging
from 0.04 to 0.36 μg l1.
Figure 19: Derivatization strategies for 3-quinuclidinol.
Unfortunately for GC-MS analysis, methylation has not been an integral part of the available toolbox for
the analysis of 3Q, and a reason for this again is the strong nucleophilicity of its nitrogen that on alkylation
becomes a quaternary salt, thus annulling any chances of detection by GC-MS means. A clever way around this
problem was devised by Vertox laboratories when they reported the use of p-tolylisocyanate (PTI, 105). The
reaction between the hydroxyl moiety and the reagent produces a stable 3Q-carbamate (106) that is amenable
for GC-MS analysis (Karthikraj et al., 2014) (Figure 19). The reaction between PTI and 3Q is rapid and efficient,
which is the reason why heating is not needed. Furthermore, an added benet of the protocol is the late eluting
character of the carbamate in the analysis that becomes important when abundant, early eluting interferences
are present in the mixture.
21
     ProofCheck     
   DE GRUYTER
Conclusions
The analysis by GC-MS means of CWAs and their degradation products has experienced a strong revitaliza-
tion in the past two decades as a result of great advances in the miniaturization of the technique in the form
of eld-deployable units and the development of new, more efficient sample preparation and derivatization
methods. More than ever in history, there is an urgent need to develop analytical tools that can detect in a swift
and efficient manner these highly toxic entities. Some of the reasons behind the concerted, focused effort on
consolidating GC-MS as a mainstream technique for the qualitative and quantitative analysis of CWAs are its
relatively inexpensive nature and its much-needed benchtop to eld-deployable unit transition. Despite the
great advances toward achieving GC-MS portability in the eld, this represents only one facet of the overall
growth of the technique to become the preferred analytical tool by combatants or rst responders to a scene
where the presence of CWAs is highly suspected. Recognition of this fact has resulted in the parallel research
efforts to discover or improve well-established derivatization protocols that are vital for routine GC-MS anal-
yses. This area of research is particularly important as degradation products arising from CWAs are mostly
imperceptible by GC-MS due to their salt-like or highly polar nature. Derivatization methods like silylation
and methylation, employing BSTFA and diazomethane, respectively, certainly made an enormous positive early
impact in the eld due to their established position in analytical chemistry. As years have passed, CWA anal-
ysis has experienced a transition from the quantitative analysis toward the rapid, qualitative identication of
these toxic species and their associated degradation products. This transition has demanded the development
of derivatization protocols that are not only efficient for the analyte of interest but also that produce non-toxic
and easily removable by-products (via evaporation or extraction) that do not interfere with the overall GC anal-
ysis. The eld is experiencing this expansion as newer, more rapid and milder derivatization techniques are
making their way into the analytical chemists toolbox providing him/her with ample choices for the analysis
of these toxic materials.
Acknowledgments
This document (LLNL-JRNL-727114) was prepared as an account of work sponsored by an agency of the United
States government. Neither the United States government nor Lawrence Livermore National Security, LLC, nor
any of their employees make any warranty, expressed or implied, or assume any legal liability or responsibility
for the accuracy, completeness or usefulness of any information, apparatus, product or process disclosed, or
represent that its use would not infringe privately owned rights. Reference herein to any specic commercial
product, process or service by trade name, trademark, manufacturer or otherwise does not necessarily con-
stitute or imply its endorsement, recommendation or favoring by the United States government or Lawrence
Livermore National Security, LLC. The views and opinions of the authors expressed herein do not necessarily
state or reect those of the US government or Lawrence Livermore National Security, LLC, and shall not be
used for advertising or product endorsement purposes.
Funding
This work was performed under the auspices of the US Department of Energy by Lawrence Livermore National
Laboratory under Contract DE-AC52-07NA27344.
References
             Organic & Biomolecular Chemistry 

                  
       Analytical and Bioanalytical Chemistry  
                   
               Journal of Chromatography.
B, AnalyticalTechnologies in the Biomedical and Life Sciences  
                
              Journalof Chromatography A 

22
     ProofCheck     
DE GRUYTER   
            Advances in Clinical
Chemistry  
              Handbook of chemical and biological warfareagent decontamination
  
                  
 Journal ofChromatography A  
                   
      Journal of Chromatography449 
                  
              
      
                        
           
Journal of Analytical Toxicology28 
                 
  NN  Drug Testing and Analysis  
                      
           Journal ofAnalytical Toxicology  
              Journal of Research of the National Bureau
Standards  
                   
          Journal of Organic Chemistry  
                Environmental Toxicologyand
Pharmacology  
                
     Journalof Separation Science  
                Journal of
Heterocyclic Chemistry  
          Journal of the American Chemical
Society  
                       
                

            Lancet 
              
               
Phosphorus, Sulfur, and Silicon and the Related Elements  
                    
           Journal of Labelled Compounds and Radiopharmaceuti-
cals  
            Autonomic and Autacoid Pharmacology
 
                  
    UPB ScienticBulletin, Series B: Chemistry and Materials Science  
               
    Journal of Chromatography A  
            Journal of Pain Research 
                 
 Biochemistry  
                  Handbookof
Toxicologyof Chemical Warfare Agents    
      Journal ofPharmacy And Bioallied Sciences  
              Journal of Analytical Toxicology 

                   
 Journal ofPharmaceutical and Biomedical Analysis  
                
           
    Journal ofChromatography. B, Analytical Technologies in the Biomedical and Life Sciences  
          Journal of Pain and Symptom Management 

           Journal ofPain and Symptom Management 

             Anesthesiology clinics ofNorth America  
      GreenesProtective Groups in Organic Chemistry      
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     ProofCheck     
   DE GRUYTER
               Journal of Chemical Research 

               Journal ofChro-
matography A  
                 
     ChemicalCommunications  
               
        Organic & Biomolecular Chemistry  
                    
   Trends in Analytical Chemistry  
               Journal of Pharmaceutical Sci-
ences  
          Advances in Chemistry Series 
                    
  Journalof Chromatography B  
               Journal of Organic Chemistry 

                Jour-
nal of the Society of Chemical Industry  
                
Journal of the Society ofChemical Industry  
                    
       Analytical and Bioanalytical Chemistry  
                  Foren-
sic Toxicology 
        Chemical and Engineering News89 
                Journal of Chromatographic
Science  
                 Chemical Reviews 

               Ency-
clopedia of analytical chemistry     
              Analysis of chemical warfare degradation products 
    
                
     Journal ofAnesthesia  
                 
              
     
                      
           
Journal of Chromatography A  
                        
    InternationalJournal of General Medicine  
                    
      Journal of Analytical Toxicology24 
                Journal of Chro-
matography B. 
           Organic Letters  
                   
        Journalof Physical Chemistry B  
                      
            Analytical
Chemistry  
               Journal für praktische Chemie  
          Military Medical Science Letters

               Environmental
Health Perspectives 
                    
      Journal of Chromatography A  
                        
               Journal of Chromatogra-
phy A  
24
     ProofCheck     
DE GRUYTER   
                   
              
 Analytical and Bioanalytical Chemistry  
                  
 Journalof Chromatography A  
               
   Journal of Chromatography A  
             
    Journal of Chromatography A  
               
      Journalof Analytical Toxicology  
                
           Journal of Chromatography A
 
                   
       Chromatographia 
                 Angewandte
Chemie International Edition  
               
    Journal of Chromatography A  
                
         Analytical Chemistry  
              
    Analytical and Bioanalytical Chemistry  
                   
       Journal of Chromatography B  
                        
     Journal of Analytical Toxicology 
              Lancet  
              
       
  Drug Testingand Analysis  
                 
         
Journal of Chromatography A  
                 Chemico-
Biological Interactions  
                     
             
 Trends in Analytical Chemistry  
                        
      Journal of Chromatography A  
               Journal of
Labelled Compounds and Radiopharmaceuticals 
                  
 Phosphorus Sulfur Silicon and the RelatedElements  
                  
 Phosphorus Sulfur Silicon and the RelatedElements  
            Journal of
Chromatography B: Biomedical Sciencesand Applications  
                    
      Heterocycles  
               
         Journal of Analytical Chemistry  
                
   Journal of Applied Toxicology  
        Toxicology  
                   
        Journal of Chromatography A  
                 
            Journal of Chromatographic Science

                 
            An-
alytica Chimica Acta  
25
     ProofCheck     
   DE GRUYTER
               β       
         Rapid Communications in
Mass Spectrometry  
                 PLoS One  
                  
     Journal of Chromatography B  
                  
    Journal ofAnalytical Toxicology  
               Annals ofEmergency
Medicine  
                  
   Journal ofChromatography B: Analytical Technologies in the Biomedical and Life
Sciences  
         Accounts of Chemical Research 
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... The determination of CWAs and their degradation products using gas or liquid chromatography in conjunction with mass spectrometry has been extensively reviewed [4][5][6][7][8][9][10][11][12]. Compared with HPLC-ICP-MS, these methods have certain disadvantages. ...
... Simplified scheme of possible hydrolysis pathways for tabun (GA) and VX[5,30]. ...
... Simplified scheme of possible hydrolysis pathways for tabun (GA) and VX[5,30]. Simplified hydrolysis scheme for RVX (S-[2-(diethylamino)ethyl] O-(2-methylpropyl) methylphosphonothioate; known as Russian VX), sarin (GB), soman (GD), and cyclosarin (GF). Starting substances (CWAs) are marked on a yellow background, intermediates are marked on a beige background, and the product of the hydrolysis of these compounds (MPA) is marked on a purple background[5,31,32]. ...
Article
Full-text available
The determination of chemical warfare agents (CWAs) and their toxic degradation products (DPs) has become increasingly important for public and military safety in recent years. We focused on assessing the possibility of the HPLC-ICP-MS analytical technique to verify the provisions of the Chemical Weapons Convention. This technique enables the identification and determination of minimal concentrations (ppt range) of elements in various matrices. This fact is important for the determination of CWAs and other highly harmful compounds, even small amounts of which can have serious consequences for living organisms. We have critically analysed the results of scientific research on the identification and quantitative determination of extremely toxic organophosphorus, organosulfur and organoarsenic CWAs, their derivatives and their degradation products using high-performance liquid chromatography (HPLC) coupled with inductively coupled plasma–mass spectrometry (ICP-MS).
... Such threat needs to be easily, rapidly and unambiguously detected in complex environments. The need to develop fast and reliable methods is timely because currently available detection technics hold serious flaws such as longtime analysis, sample preparation, lack of sensitivity, false positives, etc [18][19][20][21] 44,45 . An overwhelming majority of the reported studies were carried out with simulants to evaluate the potential of the different technologies [46][47][48][49] . ...
Article
Full-text available
In this study, we conducted colorimetric gas phase tests on real sarin and compared the results with the most commonly used simulants under identical test conditions. Our findings indicate that...
Article
The behavior of chemical warfare agents (CWAs) on urban materials, such as concrete, significantly impacts forensic and military responses to chemical incidents. This study examined the persistence and degradation mechanisms of sarin (GB), soman (GD), and sulfur mustard (HD) on three types of commonly used concrete with varying water-cement ratios. Over two months, we evaluated the effects of concrete composition, temperature, and fragment size on CWA behavior. Half-lives and activation energies for CWA dissipation were calculated under various conditions. Results showed that concrete properties and external temperature strongly influenced dissipation rates. G-series agents underwent rapid hydrolysis, forming methylphosphonates, while HD degradation involved elimination, nucleophilic substitution, and oxidation, producing several previously unreported byproducts. Smaller concrete fragments increased recovery values and accelerated degradation due to greater surface area exposure, and higher temperatures further enhanced dissipation rates, particularly for volatile agents. Differences in dissipation among concrete types were linked to their physical and chemical properties, notably water-cement ratios. This study highlights the challenges of detecting CWAs due to their rapid penetration and transformation in concrete and provides insights for improving sampling, identification, and decontamination strategies under realistic conditions.
Article
Detection of airborne chemical threats is an emerging challenge amidst the prevailing tumultuous global milieu. Extensive investigation has showcased the substantial promise of surface-enhanced Raman spectroscopy (SERS) for the on-site identification of hazardous chemicals present in liquid mediums, whether directly from a fluid source or through methodologies such as swab sampling. Nonetheless, exploration into the applicability of SERS for the detection of gas or vapor-phase chemical threats remains severely constrained. In this study, we present the successful realization of sub-parts per million (ppm) detection thresholds via SERS for hydrogen cyanide (HCN) and Tabun (GA) chemical warfare agents, facilitated by a custom-made gas sampling cell integrated with a Peltier cooling mechanism. The cooling regimen, spanning from 20 to - 17 ◦C, verified a 140-fold increase in the SERS signal for 1 ppm HCN, concurrently enabling the detection of HCN and Tabun concentrations as low as 0.25 and 0.5 ppm, respectively. Implementation of temperature modulation and controlled flow routines substantially reduced detection times down to 240 s for HCN, with prospects for further optimization. Free link until Feb 23, 2025: https://authors.elsevier.com/a/1kNhv94qrEIAv
Article
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A method for detecting mustard gas degradation products thiodiglycol (TDG) and thiodiglycol sulfoxide (TDGO) in water and sediment samples using gas chromatography-tandem mass spectrometry (GC-MS/MS) after derivatization with 1-(trifluoroacetyl)imidazole (TFAI) was described. Selected reaction monitoring mode (SRM) of tandem mass spectrometry was developed for analysis of TDG and TDGO derivatives while analysis by GC-AED was performed using the 181 nm sulfur canal. TFAI derivatization conditions were optimized and the method validated. Two derivatization agents were compared, TFAI and N,O-bis(trimethylsilyl) trifluoroacetamide (BSTFA), where derivatization using TFAI occurred quicker and under milder conditions than using BSTFA. Water samples containing TDG and TDGO were evaporated to dryness under nitrogen, dissolved in organic solvent followed by reaction with TFAI. The limit of detection (LOD) for TDG and TDGO were 0.01 and 5 ng/mL, respectively. The limit of detection for TDG was decreased by two orders of magnitude if TFAI is used for derivatization rather than silyl derivatizing agents (e.g. BSTFA). TFAI has three major advantages in comparison to BSTFA, the first is much higher sensitvity, the second is a very clean background, and the last one are very mild conditions of derivatization.
Article
Full-text available
Among the new psychoactive substances (NPS) that have recently emerged on the market, many of the new synthetic opioids have shown to be particularly harmful. A new synthetic analogue of fentanyl, N-phenyl-N-[1-(2-phenethyl)piperidin-4-yl]prop-2-enamide (acrylfentanyl), was identified in powder from a seized capsule found at a forensic psychiatric ward in Denmark. Gas chromatography with mass spectrometry (GC-MS) identified a precursor to synthetic fentanyls, N-phenyl-1-(2-phenylethyl)piperidin-4-amine; however, the precursor 1-(2-phenethyl)piperidin-4-on, was not detected. Analysis of the electron impact mass spectrum of the main, unknown chromatographic peak (GC) tentatively identified an acryloyl analogue of fentanyl. Further analyses by quadrupole time-of-flight high resolution mass spectrometry (QTOF-MS), matrix-assisted laser ionisation orbitrap mass spectrometry (MALDI-Orbitrap-MS), nuclear magnetic resonance spectroscopy (NMR) and infra-red spectroscopy (IR) confirmed the presence of acrylfentanyl (also known as acryloylfentanyl). Quantitative analysis with liquid chromatography and triple quadrupole mass spectrometry (LC-MS/MS) determined the content of acrylfentanyl in the powder, equal to 88.3 mass-% acrylfentanyl hydrochloride. An impurity observed by NMR was identified as triethylamine hydrochloride. Acrylfentanyl is sold on the Internet as a 'research chemical'. Like other synthetic fentanyls, such as acetylfentanyl, it poses a serious risk of fatal intoxication.
Article
DRUGMAKER SEPRACOR CANADA pleaded guilty in a Canadian court on May 2 to one charge of failing to provide proper workplace ventilation and will pay a U.S.$47,000 fine for the death of chemist Roland Daigle.
Article
In the course of the last decade, a substantial growth of new psychoactive substances (NPS) has been recorded. Within this group, a considerably fast growing sub-group is represented by the opioids, which are based on modifications of the fentanyl structure. In this study, identification and analytical characterization of a new fentanyl derivative, 4-fluorobutyrfentanyl (1-((4-fluorophenyl)(1-phenethylpiperidin-4-yl)amino)butan-1-one, 4-FBF), is described. Apart from the seized powder, 4-FBF was also identified in the e-cigarette liquid secured in Case 1. The concentration of the compound in the liquid was 35 mg/ml. The main component of the liquid was glycerol and nicotine was also present in the liquid. This substance was detected in seized material that originated from the illegal drug market in Poland. To the best of the authors’ knowledge, this report presents the first two analytically confirmed cases of fatal intoxication associated with 4-FBF. Case 1 was a 26-year old male drug user who was found dead at home. Case 2 was about a 25-year old female, occasional user of NPS and drugs, who was also found dead at home. The concentrations of 4-FBF in blood were 91 and 112 ng/mL and in urine 200 and 414 ng/mL. The concentrations of 4-FBF in liver and kidney were 902 and 411 ng/g, and 136 and 197 ng/g, for case 1 and case 2, respectively.
Book
This book describes nerve agents and vesicants, their decomposition and their degradation products' chemistry as well as their toxicity including a list of detection techniques of nerve agents and their degradation products. This book will present their history, toxicity, comparison between different sample preparation methods, separation techniques, and detection methods all together in a short, easy to read book, tied together by a single group doing the writing and the editing to assure smooth transition from chapter to chapter, with sufficient Tables and literature references for the reader who looks to further detail.The text will illustrate the pluses and minuses of the various techniques with sufficient references for the reader to obtain extensive detail.
Article
The effective methylation of phosphonic acids related to chemical warfare agents (CWAs) employing trimethyloxonium tetrafluoroborate (TMO•BF4) for their qualitative detection and identification by gas chromatography-mass spectrometry (GC-MS) is presented. The methylation occurs in rapid fashion (1 hour) and can be conveniently carried out at ambient temperature, thus providing a safer alternative to the universally employed diazomethane-based methylation protocols. Optimization of the methylation parameters led us to conclude that methylene chloride was the ideal solvent to carry out the derivatization, and that even though methylated products can be observed surfacing after only 1 hour, additional time was not found to be detrimental but beneficial to the process particularly when dealing with analytes at low concentrations (∼10 μg mL-1). Due to its insolubility in methylene chloride, TMO•BF4 conveniently settles to the bottom during the reaction and does not produce additional interfering by-products that may further complicate the GC-MS analysis. The method was demonstrated to successfully methylate a variety of Schedule 2 phosphonic acids, including their half esters, resulting in derivatives that were readily detected and identified using the instrument’s spectral library. Most importantly, the method was shown to simultaneously methylate a mixture of the organophosphorus-based nerve agent hydrolysis products: pinacolyl methylphosphonate (PMPA), cyclohexyl methylphosphonate (CyMPA) and ethyl methylphosphonate (EMPA) (at a 10 μg mL-1 concentration each) in a fatty acid ester-rich organic matrix (OPCW-PT-O3) featured in the 38th Organisation for the Prohibition of Chemical Weapons (OPCW) Proficiency Test. In addition, the protocol was found to effectively methylate N,N-diethylamino ethanesulfonic acid and N,N-diisopropylamino ethanesulfonic acid that are products arising from the oxidative degradation of the V-series agents VR and VX respectively. The work described herein represents the first report on the use of TMO•BF4 as a viable, stable and safe agent for the methylation of phosphonic acids and their half esters and within the context of an OPCW Proficiency Test sample analysis.
Chapter
Agent BZ is the code name for 3-quinuclidinyl benzilate (BZ), an anticholinergic ester of glycolic acid. BZ is a psychotomimetic chemical warfare agent described as an anticholinergic hallucinogen. BZ is a competitive inhibitor of the effects of acetylcholine (ACh) acting at the postsynaptic muscarinic receptors in the peripheral nervous system (PNS) and central nervous system (CNS). In the PNS, this inhibition is observed in the muscle, autonomic ganglia, and exocrine glands. BZ's ability to readily cross the blood-brain barrier causes mental status changes and delirium. BZ is one of the most potent anticholinergic psychotomimetics known with only small doses necessary to produce incapacitation. BZ at single doses of less than 1. mg produces delirium lasting several days. BZ is usually disseminated as an aerosol, and the primary route of absorption is through the respiratory system. Absorption also can occur through the skin or by gastrointestinal tract absorption. The pharmacologic activity of BZ is similar to atropine or scopolamine but with a much longer duration of action. Physicochemical properties and biological effects of BZ are described. The effect is characterized by vegetative symptoms progressing to hallucinations. Distribution of BZ in the body is preferably in the peripheral, followed by the CNS. Its mechanism of effect (toxicodynamics) is based on its interaction with cholinergic receptors in the CNS and PNS, and the resulting lack of a neuromediator-ACh. The antidotal effect against BZ intoxication is based on an increase of ACh levels caused by reversible cholinesterase inhibitors. From this group of compounds, physostigmine was used as the first antidote against BZ. However, physostigmine has a very thin margin between its therapeutic and toxic doses. Therefore, new inhibitors were developed, and acridine derivatives were found to be the most promising. From these compounds, 7-methoxytacrine (7-MEOTA) was the most effective. It is less toxic than physostigmine and tacrine and its central effect is pronounced. It was introduced in the Czech army as an antidote against BZ poisoning.
Article
Acetylfentanyl is a potent synthetic opioid analgesic that has been increasingly available in America, Europe, Japan, China, and Australia during the last years. It has no approved medical or veterinary use, but it is used illicitly around the world as a substitute of its controlled precursor, fentanyl, as well as of heroin or other related substances in opioid dependent individuals. It is available in retail or “head shops” or over the Internet by companies based mainly in China. Acetylfentanyl is available in the form of powder, tablets, and blotters, while liquid and injectable formulations have been also reported. Acetylfentanyl seizures have dramatically increased during the last 4 years, and its abuse has already caused a number of deaths in the United States, the United Kingdom, Sweden, and Japan, thus leading to its scheduling under the 1961 Single Convention on Narcotic Drugs in the United States, and some European Countries, China, and Japan since 2015. The aim of this review is to summarize the current knowledge about this drug concerning its chemistry, synthesis, prevalence, metabolism, pharmacology, and toxicology, as well as its legal status. Analytical methodologies developed for the determination of acetylfentanyl in biological specimens, as well as published or reported acetylfentanyl related cases, fatal or not, and self reports from drug users are presented.
Article
Cyclodextrins (CDs) are investigated for their ability to form inclusion complexes with the analgesic fentanyl and three similar molecules: acetylfentanyl, thiofentanyl and acetylthiofentanyl. Stoichiometry, binding strength, and complex structure are revealed through nuclear magnetic resonance (NMR) techniques and discussed in terms of molecular dynamics (MD) simulations. It was found that β-cyclodextrin is generally capable of forming the strongest complexes with the fentanyl panel. Two-dimensional NMR data and computational chemical calculations are used to derive solution-state structures of the complexes. Binding of the fentanyls to the CDs occurs at the amide phenyl ring, leaving the majority of the molecule solvated by water, an observation common to all four fentanyls. This finding suggests a universal binding behavior, as the vast majority of previously-synthesized fentanyl analogs contain this structural moiety. This baseline study serves as the most complete work on CD:fentanyl complexes to date and provides the insights into strategies for producing future generations of designer cyclodextrins capable of stronger and more selective complexation of fentanyl and its analogs.