Chemical warfare agents (CWA) are chemical substances that are used in warfare or terrorist activities to kill or seriously injure the people though their physiological effects [41]. A German scientist named Gerhard Schrader accidentally discovered the first nerve agent, Tabun in 1930. With the passes of time many other stable nerve agents have been developed by mid of 1950 and this is known as V-agent in USA nomenclature. Tabun is very poisonous among all toxic substances ever synthesized [42]. Similarly sulfur mustard (C₄H₈Cl₂S) is one of a class of chemical warfare agents known as vesicants because of their ability to form vesicles, blisters on exposed skin. The odor of nerve agent like mustard or garlic, hence it gets its common name sulfur mustard. The first use of nerve agent in war was by Afghanistan in 1979-80 and Iraq-Iran war from 1984-1987. The resulting Iraq-Iran chemical warfare was estimated more than 50,000 casualties. Immediately after the war, researchers were totally focused on studies of nerve agent CWA and their mechanisms. Efforts were made to discover new effective methods of protection against these CWA and its simulants [43] [44] [45] [46]. Table 3, describes an overview of all above mentioned toxic chemical warfare agents along with their symptoms method of exposure and toxic manifestations. CWA’s have been used at least twelve conflicts since including the first Iran-Iraq war know as Persian Gulf War. In Table 4, we mentioned some major chemical attacks and estimated value of casualties. Although a number of national and international convention have banned the development, production and stockpiling of chemical weapons. In spite of this, these toxic chemicals are still used.

Therefore Chemical Warfare Agents (CWAs) are very toxic compounds basically used to kill, injure or harm people as well other living organisms. They are also hazardous to the environment (i.e. contaminate air, water and land). Hence, there is increasing interest in the effective detection as well as degradation of these compounds [52].

Chemical warfare agent simulants are less toxic than real agents. These compounds suitable as spectral simulants that give rise to similar spectral characteristics and mimic all the properties of a CWA except for its toxicity. There is recommence interest in the environmental fate of Chemical Warfare Agents attributable to expand threat of chemical weapons use in a terrorist attack. The knowledge acquisition procedures used that influence the providence of Chemical warfare agents such as sulfur mustard, Lewisite, Tabun, Sarin, Soman, VX etc. in the environment are important for evolution of demolition strategies and exposure evaluations. Hence, it is necessary to extremely examine the behavior of Chemical agent by using their simulants because of the toxicity of the agents and diminution. An ideal simulant is the one which shows all the major chemical and physical properties of the CWA without any toxic or lethal properties. No definite simulant is ideal because a single simulant cannot effectively represent all environmental fate properties of a given CWA. Thus, depending on the concerned physical-chemical property, a number of different chemicals are used as chemical warfare agent’s simulants [52] [63] [64]. List of some common simulents are shown in Table 6.

Some essential physical and chemical properties of Chemical Warfare Agent are given in Table 7, which provides useful information about particular agent. A verity of compounds has been used as simulent for CWA on the basis of their physico-chemical properties.

Decontamination is a complex process and can be considered in different ways. Some basic fundamental methods of decontamination of chemical warfare agents are physical decontamination, mechanical decontamination, biological decontamination and chemical decontamination (Figure 9). Decontamination means a method used to reduce or remove and destroy the toxic nature of chemical agents [72]. Different CWAs are degraded by different chemical processes [73].

HD gas is degraded by dehydrohalogenation (CaO have this property and thus used against the degradation of CEES), aerobic oxidation by the help of catalyst [74], oxidation by using hydrogen peroxide, photo oxidation (TiO₂ have this property). G agents are degraded by two methods: enzymatic hydrolysis and non-enzymatic hydrolysis. In enzymatic hydrolysis organophosphorous hydrolase enzyme (microbial degradation) is involved [75]. Such catalyst yields large amount of acidic products therefore buffer is required to maintain the pH of the reaction in neutral to slightly alkaline range [76]. Non-enzymatic hydrolysis involves chemical compounds (i.e. iodosylcarboxylates) that promote catalytic hydrolysis in which nucleophilic substitution and hydrolysis reaction takes place [77].

A survey of literature revealed that zeolites and composite of zeolites play an important role in the welfare of society and emerged as an important field of research due to their diversified applications as these are completely safe and natural material. A lot of research work has been carried out for the degradation of chemical warfare agents by different materials (e.g. metal oxides like MgO [52] [78] [79] [80], CaO [81], Al₂O₃ [82], ZnO [83], lanthanum oxide and Fe₂O₃ [84], Y₂O₃ [85], nanorods [86], nanotubes [87] [88], nanobelts [89], detoxifying catalyst and reactive polymers [73] [90] ). However, a little effort has been made to synthesize zeolites or its derivatives (doped with either by metal oxides [91] or polymers [92] ). This fact has prompted us to synthesize some new metal oxide doped zeolites for the degradation of CWAs.

F. Carniatoa et al. [93] (2018) have been reported a class of heterogeneous naturally originated and commercially available catalysts bentonite which contain at least 80 wt% of montmorillonite clay. It was designed selectively transform toxic organosulfur and organophosphorus CWAs into non-toxic products at mild conditions and shows negligible effect on health as well as on environment. It was also performed oxidative abetment of 2-chloroethyl ethyl sulphide (CEES), well known simulant of HD in presence of H₂O₂ as an oxidant. Furthermore decontamination formulation was studied by mixing sodium perborate as an oxidant with iron bentonite. This study conceded a good decontamination test surface among CWAs and about 80% contaminated degradation within 24 hours under ambient conditions.

V.p* = Vapour pressure, F.p* = Freezing point B.p* = Boiling point, V.d* = Vapour density, M.W* = Molecular mass, P.s* = Physical state.

S. Abdul Majid et al. [94] (2018) reported sorption efficiency of mordenite versus zeolite-A on nitrate and phosphate. Sorption experiments were investigated between KH₂PO₄, NH₄NO₃ on surface modified zeolite-A and mordenite. For sorption study batch equilibrium method was adopted. Experiment was performed at a range of pH 3, 5, 7, 9 and 11. The results obtained after investigation suggested that the sorption increases with increase in pH values from 3 to 7 and the equilibrium was attained after about 12 hs. It was also found that the sorption percentage increases when the temperature is raised up to 40. Theoretical studies have also implored for mordenite and results are compared with experimental data which helps to explain the respective relation with sorption capacity and efficiency of the ions.

Y. Liu et al. [95] (2018) the detoxification ability of flexible and breathable poly (m-phenylene isophthalamide) (PMIA) loaded with MgO nanoparticles was demonstrated by gas GC-MS. They found that after 20 h of reaction time approximately 70.56% of the mustard gas surrogates have been decomposed.

M. Florent et al. [96] (2017) reported an investigation on removal of chemical warfare agent (CWA) surrogates by highly porous carbon textiles. The surface morphology of modified carbon cloths was studied and found that the modified materials has capabilities to remove 2-chloroethyl ethyl sulfide (CEES) and diethyl sulfide (EES), two sulfur mustard gas simulants. The experiment was performed in vapor phase, which might be the circumstances of the real life arrangement of mustard gas. For investigation of reaction was carried out by FTIR, XRD, nitrogen adsorption isotherm, BET, potentiometric titration, TGA and GC-MS techniques. The degradation of CEES through hydrolysis and EES is adsorbed in the nylon’s amides framework network.

Li Jixiang et al. [97] (2017) reported novel efficient and cost-effective magnetic polymer composite macro particles with highly porous activated carbon carrier adsorbent (CsFeAC) was synthesized by using the sol-gel method. It was found that synthesized polymer composite have higher specific surface area and lower crystalinity which enhance the absorption capacity. Due to its higher capacity of adsorption towards Cu²⁺ ions present in water causes a serious threat to the environment and human beings. In this study it was found the adsorption data match better with the Langmuir adsorption isotherm and it shows adsorption is a monolayer adsorption. Furthermore, kinetics studies show that the adsorption adopts the pseudo-second order kinetics.

M. Sadeghi et al. [98] (2016) in this study, zinc oxide nanoparticles (ZnO NPs) have been surveyed to decontaminate the chloroethyl phenyl sulfide (CEPS simulent of sulfur mustard) as a sulfur mustard agent simulant. Prior to the reaction, ZnO NPs were successfully prepared through sol-gel method in the absence and presence of polyvinyl alcohol (PVA). PVA was utilized as a capping agent to control the agglomeration of the nanoparticles. The formation, morphology, elemental component, and crystalline size of nanoscale ZnO were certified and characterized by SEM/EDX, XRD and FT-IR techniques. The proposed mechanism is given in Figure 10.

M. St’astny et al. [99] (2016) used manganese (IV) oxide for degradation of toxic organophosphorus compounds which was prepared by homogeneous hydrolysis of KMnO₄ with 2-chloroacetamide. The degradation efficiency was determined with parathion methyl using HPLC and for comparative study, synthesized manganese (IV) oxides by direct method (reaction of MnSO₄·H₂O and KMnO₄, and reaction of KMnO₄ with urea in aqueous solution). The sample of KMnO₄ with 2-chloroacetamide showed the greatest degradation efficacy of about 90% within 2 h. Reaction mechanism shown in Figure 11.

M. Sadeghi et al. [100] (2016) have been reported the performance of NiO NPs/Ag-clinoptilolite zeolite as a novel composite adsorbent for the decontamination of two most known sulfur mustard (nerve agent) simulants 2-chloroethyl ethyl sulfide (CEES) and dimethyl methyl phosphonate (DMMP). The reactions were carried out in both methanol and n-hexane solvents and monitored by GC-FID, 31P-NMR and GC-MS analyses subsequently. Moreover, the SEM/EDAX, XRD and FT-IR techniques were applied for characterization of prepared samples. The GC-FID results reveal that the composite material (NiO NPs/Ag-clinoptilolite zeolite) in normal hexane solvent shows excellent 86% decontamination in 12 h at room temperature toward CEES and 31P NMR data reveals that more than 89% decontamination of DMMP within 8 h was found at similar conditions. The calculated value of rate constant and half-life for CEES and DMMP was found 3.8194 × 10⁻⁵ s⁻¹, 7.3055 × 10⁻⁵ s⁻¹ and 1.8640 × 10⁴ s⁻¹, 9.4860 × 10³ s⁻¹ respectively. The product formed during hydrolysis i.e. hydroxyl ethyl ethylsulfide (HEES) and methyl phosphoric acid (MPA) was recognizing by GC-MS analysis.

A. Hiromichi et al. [101] (2016) reported synthesis of mordenite zeolite and its composite material using for toxic Cs ion decontamination. Reagents SiO₂ and NaAlO₂ used for synthesis without addition of a template and a seed powder. In this reaction, obtained mordenite contains Al/Si ratios 0.085:0.120 was found, at temperature range between 170˚C to 200˚C for 24 h. Initially Mordenite zeolite (1.0 g) show greater than 99% and 85% - 92% adsorption capacity for 100 ppm Cs⁺ (100 mL) solutions of water and seawater respectively. The Cs⁺ cation exchange capacity was found 180 - 210 cmol kg (centi moles of charge per kilogram) and it increases with varying Al/Si ratio. Furthermore for the magnetic collection composite material of the mordenite and magnetite of 10, 20 and 30 wt% was synthesized and tested for decontamination. It was observed that total Cs⁺ ion decontamination rates were also high (more than 95%) by using the magnetic collection material after the Cs⁺ adsorption in water. Mordenite zeolite has been found very effective adsorbent for radioactive Cs⁺ ion decontamination because of high selectivity. The cation exchange capacity and the Cs⁺ adsorption ability in seawater was found in good agreement compared to the synthesized mordenite from diatomite and the natural mordenite because of the low impurities for the material made from the chemical reagents.

K. Dastafkan et al. [102] (2015) reported 20 wt% MnO₂NPs-AgY zeolite catalysts in different solvents for decontamination reactions of O,S-diethyl methyl phosphonothiolate (OSDEMP), as an agricultural organophosphorus pesticide. This reaction was studied by GC-FID and GC-MS techniques. The catalyst was synthesized in three different steps: in first step, Na-Y zeolite was prepared by hydrothermal method. In second step, by using ion exchange procedure Ag-Y zeolite was prepared from Na-Y zeolite. In final step, MnO₂NPs were synthesized by doping of Ag-Y zeolite into manganese (II) nitrate solution. The confirmation of the synthesized material and nanocomposite catalyst was characterized through SEM, XRD, AAS and FTIR spectroscopy techniques. In this study it was found MnO₂NPs-AgY zeolite composite catalyst (20 wt%) has capacity to convert OSDEMP into a less toxic or non-toxic product. Adsorption, degradation and hydrolysis reactions were studded in different solvents and time intervals at normal temperature and pressure conditions. The procedure for reaction was given in Figure 12 and reaction mechanism is shown in Figure 13. This study concludes synthesized 20 wt% MnO₂NPs-AgY zeolite nanocomposite has greater decontamination efficiency towards OSDEMP molecule and it was also found that OSDEMP molecule was perfectly decontaminated (100%) in n-heptanes solvent after 8 hours.

V. V. Singh et al. [103] (2015) reported CWAs (diethyl chlorophosphate) and BWAs (against E. coli bacteria) detoxification by using silver-exchanged zeolite (AgZ) micromotors. Such multifunctional reactive Ag-zeolite micro-motors are highly efficient on-the-fly for detoxification strategy of chemical and biological threats under ambient conditions. The synthesized new Ag-zeolite micro motor was very much effective towards detoxification of CWAs. The combination of Ag-zeolite micromotors catalyst reflects effective adsorption capacity due to embedded Ag⁺ ion and the dynamic moment behavior of the micro motors. The synthesized Ag-zeolite micro motors have a specific function and its components are useful practically sustainable, economical, and eco-friendly. All the studies clearly indicated that the presence of micropores and high surface area of the zeolite facilitate the adsorption of DCP molecules within it. Also the presence of Ag⁺ (also have antibacterial activity) leads to stronger interactions and accelerated chemisorptions process. The mechanism of this process is shown in Figure 14. These properties and capabilities of zeolite micro motors make it advantageous over recently developed motors and lead to detoxification and to green degradation products.

J.P. Kumar et al. [104] (2015) synthesized and compared degrading ability (HD gas) of eight different metal oxides (i.e. MgO, CaO, NiO, CuO, Ag₂O, MnO₂, CeO₂ and Fe₂O₃) and doped with 13-X zeolite. Zeolites were characterized by the help of XRD, TEM and SEM-EDAX while the decontamination reactions were studied by the help of GC and GC-MS. TEM images depicted different shapes of various MO_X-13X materials. Nanorods in case of NiO-13X while nanobelts in MnO₂-13X and MgO-13X. XRD graph patterns showed no changes in crystal structure of zeolite by doping with metal oxides. It was also found that surface area has decreased after doping with metal oxide nano-particles and shows better reactivity against decontamination of HD. This is due to blocking of micropores which cause the decrease of micropore volume. The data in Table 8 shows decontamination efficiency. Maximum efficiency was shown by Ag₂O-13X which degraded 100% of HD gas in 16 h.

This unusual efficiency of silver oxide has been explained. Silver ion abstracts chloride ion from HD gas and thus convert it into its degraded products. It was found that silver ion possess relatively higher affinity towards sulfur atom of HD as compared to other metal ions. GC-MS has confirmed that on bare Na-13X zeolite only hydrolysis reaction takes place on its surface while in MO_X-13X materials have elimination as well as hydrolysis reactions. Reaction of HD on Na-13X results the formation of HM (hemisulfur mustard) and TDG (thiodiglycol) products. While on reaction with MO_X-13X materials, six different products (1,4-oxathiane, chloroethyl vinyl sulfide, hydroxyl ethyl vinyl sulfide, HM, TDS and divinyl sulfide) were formed. Proposed mechanism is shown in Figure 15.

M. Sadeghi et al. [91] (2014) have synthesized MnO₂-AgX zeolite nanocomposites. It was a novel adsorbent catalyst for the decontamination against 2-CEPS and 2-CEES (sulfur mustard simulants). The reaction mechanism for the decontamination of Sulfur mustard simulants are shown in Figure 16(a) and Figure 16(b). Crystalline size and morphology were explained with the help of SEM, AAS, GC-FID, GC-MS and GC analysis. Above characterization techniques reveals that the amounts of silver (10.3 wt%) and manganese (18.4 wt%) were sufficient for complete decontamination (100%) within 12 h and changes these toxic simulants into non toxic products.

W. A. Khanday et al. [105] (2014) reported the adsorption of dimethyl methyl phosphonate (DMMP) over synthetic zeolite-α. It was observed that initially adsorption of DMMP was found to be high and then it decreases with an increase in the injection volume. Thus adsorption rate was increases with increase in the contact time between zeolite-α and DMMP. The reaction mechamism is shown in Figure 17. Zeolite-α shows equilibrium time up to 8 h and after reaching equilibrium, the adsorption rate become almost constant. Further desorption experiment was performed and completed successfully the data demonstrate that desorption exhibit from both strong and weak adsorption sites.

W. A. Khanday et al. [106] (2013) have been reported that Zeolite-A, Zeolite-X, MCM-22 and Erionite were synthesized by hydrothermal methods and were characterized successfully by X-ray diffraction (XRD), Fourier transform infrared (FTIR) spectroscopy, scanning electron microscopy (SEM), Brunauer-Emmett-Teller (BET) surface area analysis, energy dispersive spectroscopy (EDS) and thermal programmed desorption (TPD). The adsorption of dimethyl methyl phosphate (DMMP) was performed on these synthesized zeolites. The adsorption data demonstrated that highest surface area among all zeolites was shown by Zeolite-X and having highest adsorption capacity followed by Erionite and MCM-22 whereas Zeolite-A shows the least surface area and having least adsorption capacity. On comparing the surface area of synthesized zeolite the order of increasing surface area was found: Zeolite-X > Erionite > MCM-22 > Zeolite-A. In this study it was also found that initially adsorption rate was found to be high for all zeolites and then it decreases with increase in injected volume. Further desorption study was carried out successfully and two types of desorption pattern peaks were observed. The sharp peaks of desorption pattern representing desorption of physisorbed DMMP and broad peaks representing desorption of strongly chemisorbed DMMP. The mechanism of reaction is shown in Figure 18.

S. L. Sharifi Alhashem et al. [107] (2012) have been investigated decontamination of diethyl methyl phosphonate (DEMP,) and 2-chloroethyl phenyl sulfide (CEES) (simulent of Sulphur mustard, HD) by using nano-MnO₂/Zeolite AgY composite. It was found that, in first case 2-CEPS was produced about 86% by composite after 24 h, and it changed to less toxic chemical products Figure 19(b) and in second case absorption of DEMP was found nearly 87% after 30 h Figure 19(a). Results are identified by GC-MS and proton NMR respectively.

R. Satya Agarwal et al. [92] (2012) have been reported the detoxification of Paraoxon (simulent of sarin, nerve agent) by functionalized cellulose/ PET polymer/ zeolites (Linde type A and Mordenite). The stimulant paraoxon detoxification studies by functionalized membranes were successfully obtained.

The prepared paraoxon stock solution shows UV absorbance value at 6.8 nm. After adding prepared functionalized cellulose/PET polymer/zeolites fibers to stock solution of paraoxon, a decrease in the UV absorbance value of paraoxon solution was observed within time interval of 15 min and 1 hour. This decrease in the UV absorbance value shows that the catalyst containing nanofibers has the capacity to detoxifying harmful agent like organophosphorous. This concludes, functionalized cellulose/PET polymer/zeolites are tested for the decontamination of nerve agent simulant Paraoxon, and stimulant gets hydrolyzed. The rates of hydrolysis for different organophosphate hydrolyzing agents are compared and it was found that the reactivity and amount of adsorption of these catalysts are of higher.

J. Zhang et al. [108] (2012) have studied the effects of Surface and morphological properties and impedance change on zeolite (NaY) and cerium oxide coating zeolite material towards DMMP (dimethyl methyl phosphonate). Comparative study of three zeolite sensors including pure NaY zeolite based, NaY coated with 30% CeO₂ and 3 µm films was used for detection of ~100 ppm DMMP at 320˚C at fixed frequency of 3 kHz. On increasing the concentrations of CeO₂, impedance remained unchanged but response time was increased. It was found that membrane of zeolite based material show greater response in comparison to the pressed pellets of NaY and CeO₂-coated NaY. Finally it has reported that cerium oxide coating can successfully improve the recovery feature of the sensors, leading to desorption of DMMP.

Y.C Hudiono et al. [109] (2012) a new composite material was synthesized which act as highly breathable barrier material against mustard agent simulant (2-CEES). This composite material consists of two components: diol-RTIL polymer (a cross linked diol-functionalized room temperature ionic liquid polymer) and zeolite (NaY). The hydroxylated polymer component renders high water vapor penetrability whereas the basic zeolite renders reactive blocking of CEES vapor.

Ji. Xinming et al. [110] (2011) have reported adsorption-desorption behavior of Nanozeolites i.e. silicate-1, ZSM and Cu-ZSM-5 as adsorbent for DMMP (Dimethyl Methyl phosphonate). It has been found that Cu-ZSM-5 had highest adsorption capacity and best selectivity due to increase in proportion to copper content. The sensitivity and detection limit was observed with Cu-ZSM-5 about 8.8 Hz/ppm and 0.3 ppm, respectively, which confirm that zeolite Cu-ZSM-5 is good adsorbent for the detection of DMMP. The maximum adsorption capacity of Cu-ZSM was found when the copper content was more than 2.72%.

B. Nazari et al. [111] (2010) have been reported comparative study of MgO particles synthesized in laboratory and technical grade. The method of synthesis was used very easier and effective. The ability of different types of MgO particles for the destruction of chemical warfare agents (CWA) simulants malathion (VX simulant) and DMMP (GB simulant). In this investigation it was found that the weight ratios of 1:16 and 1:32 (stimulant: MgO particles) decompose almost all of the CWA simulants. It was also found that the weight ratio of 1:32 could destroy the other destruction products. The characterization techniques UV-Vis and BET used for investigation. BET analysis showed that specific surface area (SSA) of the synthesized MgO particles and technical grade of MgO powders was found ~30.96 m²/g and ~166.86 m²/g respectively and synthesized MgO particles and technical grade of MgO powders had an average particle size of 75 nm and 20 micrometers, respectively. This study concludes that MgO particles showed a greater potential in the destruction of simulants of chemical warfare agents with a simple and low cost effective method.

L. Bromberg et al. [90] (2009) reported the compound PANOx and PHA were very reactive and obtained by one-step oximation of polyacrylonitrile and polyacrylamide, respectively. Synthesized compound polyacrylamidoxime (PANOx) and poly (N-hydroxyacrylamide) (PHA) shows nucleophilic hydrolysis towards chemical warfare agents (CWA) S-2-(diisopropylamino) ethyl O-ethyl methylphosphonothioate (VX), O-pinacolyl methylphosphonofluoridate (Soman, or GD), and isopropyl methylphosphonofluoridate (Sarin, or GB). The specific synthesized polymers (PANOx and PHA) were converted into their corresponding oximate salts which have greater pH values than the pKa i.e. 7.5 and 10.8 respectively. The synthesized PANOx and PHA showed spontaneous hydrolysis at moderate temperature and humidity. The conversion of the hydroxamate into the unreactive carboxylic groups was insignificant, so that the polymers maintained reactivity at mild conditions. The half-lives of VX in heterogeneous hydrolysis were measured in the presence of PANOx and PHA from 0.093 to 4.3 and 7.7 h, which obey pseudo-first order kinetics in the polymer dispersions. The rates of hydrolysis of PANOx towards VX exhibited a strong dependency on the degree of conversion of the amidoxime to amidoximate groups and in case of GB half-life was found less than 3 min. The nontoxic nature, greater catalytic efficiency and mode of synthesis for PANOx and PHA polymers make them attractive materials in decontamination. The degradation pathway is shown in Figure 20(a) and Figure 20(b). This study concludes the compounds PANOx and PHA are obtained by a simple oximation method with high yields and contain 3 - 10 mmol of reactive groups (amidoximate or hydroxamate) per gram of dry polymer.

In the presence of water, PANOx and PHA hydrolyzed GD and VX with great interest having half lives shorter than those in alkaline water. Due to simplicity in synthetic process, low cost of the precursor and greater degradation efficiency makes PANOx and PHA attractive in today’s scenario.

H. Grassian et al. [7] (2008) has reported the degradation of DMMP (dimethyl methyl phosphate, simulant of Sarin) nerve agents and 2-CEES (2-chloroethyl ethyl sulphate, simulant of sulfur mustard) blister agents by using three different nanocrystalline zeolites i.e. NaY, NaZSM-5 and silicalite. Nanocrystalline NaZSM-5 was found better degradent than the other two zeolites. It was found that CEES was decomposed by all the three zeolites (NaZSM-5, silicalite and NaY zeolite) whereas DMMP was degraded by only NaY zeolite. The adsorption was monitored by flow reactor apparatus and thermal conductivity detector (TCD) of GC. NaZSM-5 shows greater reactivity than silicalite. 20% more 2-CEES was adsorbed on its surface as compared to silicalite.

A. Kilincarslan et al. [112] (2007) reported synthesized PAN/zeolite composite has good adsorption capacity towards Th(IV) from aqueous solutions by using a batch technique. The parameters use for thorium adsorption was studied as pH, concentration, shaking time and temperature. The interpreted data fit into Langmuir, Freundlich and D-R type adsorption and desorption isotherms. In this study it was found with hydrochloride acid solution, desorption of Th(IV) is very slow and percent for this adsorbent was only found 14.48%. As a result of this, creating different chemical forms of Th(IV) with some components of the composite adsorbent and investigated the adsorption process. This study concludes that adsorbent is low cost and very effective sorbent for Th(IV) ions and the synthesized PAN/zeolite composite adsorbent exhibited excellent adsorption for Th(IV).

K. Knagge et al. [113] (2006) have been reported the thermal degradation of nerve agent simulant dimethyl methylphosphonate (DMMP) by using Nanocrystalline NaY. 31P MAS NMR study reported the formation of two non toxic phosphorus species i.e. DMP and HMPA. After complete thermal decomposition of DMMP, the disappearance of all these products with the exception of some strongly adsorbed phosphate species was observed. Adsorption and thermal reaction of DMMP in Nanocrystalline NaY with a crystal size of ∼30 nm. DMMP adsorbs molecularly in nanocrystalline NaY at 25˚C. The FTIR spectroscopy of Gas-phase products of the reaction of DMMP and oxygen in Nanocrystalline NaY at 200˚C was carried out and determined to be carbon dioxide (major product), formaldehyde, and dimethyl ether as products. The reactivity ratio per gram of zeolite sample was comparable to other recent studies of metal oxides like MgO, Al₂O₃ and TiO₂. The reaction mechanism is shown in Figure 21.

W. George et al. [114] (1999) investigate the reactions of synthesized zeolites NaY and AgY with CW Agent VX, HD and their simulants DEPPT (O,S-diethyl phenylphosphonothioate) and CEPS (2-chloroethyl phenyl sulfide) at room temperature. The reaction mechanisms are shown in Figure 22(a) and Figure 22(b). NMR techniques (solid-state magic angle spinning) were used to study the reaction.

VX molecules undergo hydrolysis with NaY and AgY zeolites and ultimately cleavage of the P-S to yield EMPA (ethyl methylphosphonate) which was slowly convert into ethyl 2-(diisopropylamino)ethyl methylphosphonate. Similar reaction was observed for DEPPT on AgY and silver salt of ethyl phenylphosphonate was observed but DEPPT does not show reaction with NaY. Hence AgY catalyzed hydrolysis reaction was more appropriate for both VX and DEPPT. In Case of HD and CEPS the reactivity of NaY was more as compare to AgY and formed Toxic CH-TG sulfonium ion and non toxic HEPS (2-hydroxyethyl phenyl sulfide) product respectively. In Case of VX hydrolysis of the P-O bond was not observed on either AgY or NaY and the desulfurized by-product yield was found 78%.

The bluff of terrorist attacks and environmental hazards has drawn attention of research scientists towards study of CWA and their simulants. The number of papers was comprised in this review related to decontamination study of CWA and simulants of CWA. Zeolite materials, metal oxides and composites of zeolites due to their readily availability, user-friendly and eco-friendly nature have been the subjects of such studies, and various zeolite materials have been investigated in this regard. Nano-technology could also open a new window for serial formulations with intensify advantages like high surface area, high ion exchange capacity and high surface to volume ratio towards CWA. Nanoscale zeolite are

more effective because of the presence of large surface area and pore volumes, low crystal defects, high ion exchange capacity etc. The products of degradation of CWA simulants on zeolite nanosurfaces have been examined experimentally. The correlation between the results for the real agents and their simulant implies that experiments performed with the simulant can be extrapolated to understand the mechanism for the real agents. Though large number of experimental results regarding the adsorption and degradation/decontamination of CWA on nanoscale zeolite and their simulants has accumulated over the years, this work has to be done to find materials for the early detection and degradation/decontamination of CWAs as well its simulants. In particular, large porous size and surface area zeolite and doped zeolite nanoparticles need to be explored further, as they have shown promise as future materials for CWA adsorption and degradation. Further research is necessary to determine the yet undetermined parameters like adsorption behaviour and mechanisms in zeolite-composite reactions.

Conflict of interest on behalf of all co-authors, the corresponding author states that this article content has no conflict of interest.

I acknowledge all the co-authors of this article particularly my mentor for supporting me to make this review paper possible.

Kumar, N., Tiwari, K.R., Meenu, Km., Sharma, A., Jain, A., Singh, S. and Tomar, R. (2019) Utilization of Various Analogy of Synthetic Nanoporous Zeolites and Composite of Zeolites for Decontamination/Detoxification of CWA Simulants—An Updated Review. International Journal of Nonferrous Metallurgy, 8, 35-71. https://doi.org/10.4236/ijnm.2019.84004