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Cas Database

7647-01-0

7647-01-0

Identification

  • Product Name:Hydrogen chloride

  • CAS Number: 7647-01-0

  • EINECS:231-595-7

  • Molecular Weight:36.4609

  • Molecular Formula: HCl

  • HS Code:2086.10

  • Mol File:7647-01-0.mol

Synonyms:UN 2186 (refrigerated liquefied gas);Hydrochloric acid [JAN];Chlorwasserstoff [German];Chlorohydric acid;Hydrochloric acid 36% by weight or more HCl;Hygeia Creme Magic Bowl Cleaner;Aqueous hydrogen chloride;Hydrogen chloride (gas only);UN 1789 (solution);Anhydrous hydrochloric acid;Hydrogen chloride, anhydrous [UN1050] [Poison gas];Hydrochloric acid, solution [UN1789] [Corrosive];Chloruro de hidrogeno [Spanish];Hydrogen chloride (HCl);Muriatic acid;Wuest Bowl Cleaner Super Concentrated;Hydrochloride;Ethanol,2-[2-[2-[4-[(4-chlorophenyl)phenylmethyl]- 1-piperazinyl]ethoxy]ethoxy]-;Now South Safti-Sol Brand Concentrated Bowl Cleanse with Magic Actio;Chlorure dhydrogene [French];Percleen Bowl and Urinal Cleaner;Synthetic hydrochloric acid;Hydrogen Chloride Anhydrous;

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Safety information and MSDS view more

  • Pictogram(s):ToxicT, CorrosiveC, FlammableF, IrritantXi, HighlyF+

  • Hazard Codes: C:Corrosive;

  • Signal Word:no data available

  • Hazard Statement:no data available

  • First-aid measures: General adviceConsult a physician. Show this safety data sheet to the doctor in attendance.If inhaled Fresh air, rest. Half-upright position. Artificial respiration may be needed. Refer immediately for medical attention. In case of skin contact Wear protective gloves when administering first aid. First rinse with plenty of water for at least 15 minutes, then remove contaminated clothes and rinse again. Refer immediately for medical attention. In case of eye contact Rinse with plenty of water for several minutes (remove contact lenses if easily possible). Refer immediately for medical attention. If swallowed Never give anything by mouth to an unconscious person. Rinse mouth with water. Consult a physician. Inhalation of fumes results in coughing and choking sensation, and irritation of nose and lungs. Liquid causes burns. (USCG, 1999)Gas concentrations of 50 to 100 ppm are tolerable for 1 hour. Concentrations of 1,000 to 2,000 ppm are dangerous, even for brief exposures. More severe exposures will result in serious respiratory distress and prolonged exposures will result in death. Mists of hydrochloric acid are considered less harmful than anhydrous hydrochloric acid, because droplets have no dehydrating action. Individuals with respiratory problems and digestive diseases may be adversely affected by low level exposures to the gas or mist. (EPA, 1998)Excerpt from ERG Guide 125 [Gases - Corrosive]: TOXIC; may be fatal if inhaled, ingested or absorbed through skin. Vapors are extremely irritating and corrosive. Contact with gas or liquefied gas may cause burns, severe injury and/or frostbite. Fire will produce irritating, corrosive and/or toxic gases. Runoff from fire control may cause pollution. (ERG, 2016)SYMPTOMS: Symptoms of exposure to this compound include mild irritation of the skin and eyes, diarrhea and gastrointestinal irritation. It may also cause nausea, pulmonary edema and coma. Gastrointestinal disturbances may occur. ACUTE/CHRONIC HAZARDS: This compound is a mild irritant of the skin and eyes. When heated to decomposition it emits toxic fumes of nitrogen oxides, sulfur oxides and ammonia. /PREHOSPITAL/ Consult with the base station physician or the regional poison control center for advice regarding triage of multiple victims. Patients with evidence of significant exposure such as skin or eye irritation, pain, or breathing difficulties should be transported to a medical facility for evaluation. Others may be discharged from the scene after their names, addresses, and telephone numbers are recorded. Those discharged should be advised to seek medical care promptly if symptoms develop

  • Fire-fighting measures: Suitable extinguishing media Suitable extinguishing media: Use water spray, alcohol-resistant foam, dry chemical or carbon dioxide. Special Hazards of Combustion Products: Toxic and irritating vapors are generated when heated. (USCG, 1999)Fire may produce irritating or poisonous gases. Containers may explode in heat of fire. At high temperatures, it decomposes into hydrogen and chlorine. The following materials should be avoided: Mercuric sulfate -- violent reaction with gaseous hydrochloric acid at 250F. Sodium -- reacts vigorously with gaseous hydrochloric acid. Acetic anhydride, 2-aminoethanol, ammonium hydroxide, chlorosulfonic acid, ethylene diamine, ethyleneimine, oleum, propiolactone, sodium hydroxide, sulfuric acid, and vinyl acetate -- increase in temperature and pressure when mixed with hydrochloric acid. Calcium phosphide -- energetic reaction with hydrochloric acid. Silver perchlorate and carbon tetrachloride -- when mixed in combination with hydrochloric acid forms a compound that detonates at 105F. Formaldehyde -- when mixed with hydrochloric acid forms a human carcinogen. Material reacts violently with bases and is corrosive with the generation of heat. Reacts with base metals, forming combustible gas (hydrogen). Reacts violently with strong oxidants forming toxic gas (chlorine). Avoid heat; at high temperatures it will decompose into hydrogen and chlorine. (EPA, 1998)Excerpt from ERG Guide 125 [Gases - Corrosive]: Some may burn but none ignite readily. Vapors from liquefied gas are initially heavier than air and spread along ground. Some of these materials may react violently with water. Cylinders exposed to fire may vent and release toxic and/or corrosive gas through pressure relief devices. Containers may explode when heated. Ruptured cylinders may rocket. For UN1005: Anhydrous ammonia, at high concentrations in confined spaces, presents a flammability risk if a source of ignition is introduced. (ERG, 2016)This chemical is probably combustible. Wear self-contained breathing apparatus for firefighting if necessary.

  • Accidental release measures: Use personal protective equipment. Avoid dust formation. Avoid breathing vapours, mist or gas. Ensure adequate ventilation. Evacuate personnel to safe areas. Avoid breathing dust. For personal protection see section 8. Evacuate danger area! Consult an expert! Personal protection: gas-tight chemical protection suit including self-contained breathing apparatus. Ventilation. Remove gas with fine water spray. Accidental release measures. Personal precautions, protective equipment and emergency procedures: Wear respiratory protection. Avoid breathing vapors, mist or gas. Ensure adequate ventilation. Evacuate personnel to safe areas.; Environmental precautions: Prevent further leakage or spillage if safe to do so. Do not let product enter drains.; Methods and materials for containment and cleaning up: Clean up promptly by sweeping or vacuum.

  • Handling and storage: Avoid contact with skin and eyes. Avoid formation of dust and aerosols. Avoid exposure - obtain special instructions before use.Provide appropriate exhaust ventilation at places where dust is formed. For precautions see section 2.2. Cool. Fireproof if in building. Separated from food and feedstuffs and incompatible materials. See Chemical Dangers. Keep in a well-ventilated room.Keep container tightly closed in a dry and well-ventilated place. Storage class (TRGS 510): Gases

  • Exposure controls/personal protection:Occupational Exposure limit valuesRecommended Exposure Limit: Ceiling value: 5 ppm (7 mg/cu m).Biological limit values Handle in accordance with good industrial hygiene and safety practice. Wash hands before breaks and at the end of workday. Eye/face protection Safety glasses with side-shields conforming to EN166. Use equipment for eye protection tested and approved under appropriate government standards such as NIOSH (US) or EN 166(EU). Skin protection Wear impervious clothing. The type of protective equipment must be selected according to the concentration and amount of the dangerous substance at the specific workplace. Handle with gloves. Gloves must be inspected prior to use. Use proper glove removal technique(without touching glove's outer surface) to avoid skin contact with this product. Dispose of contaminated gloves after use in accordance with applicable laws and good laboratory practices. Wash and dry hands. The selected protective gloves have to satisfy the specifications of EU Directive 89/686/EEC and the standard EN 374 derived from it. Respiratory protection Wear dust mask when handling large quantities. Thermal hazards

Supplier and reference price

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Relevant articles and documentsAll total 262 Articles be found

Cristol

, p. 338,341 (1947)

Coombe, R. D.,Pritt, A. T.,Pilipovich, D.

, p. 345 - 348 (1975)

Catalytic Activity of Bismuth(III) Chloride for Dehydrochlorination of Poly(vinylchloride)

Uemichi, Yoshio,Takuma, Kazuhiko,Sugioka, Masatoshi,Kanazuka, Takaji

, p. 735 - 737 (1991)

Bismuth(III) chloride was found to be highly active as a catalyst for the dehydrochlorination of poly(vinylchloride).The degree of dehydrochlorination was 97percent at the highest.The catalyst showed high activity even in water vapor.

Thermal dehydration and decomposition of FeCl3·xH2O

Kanungo,Mishra

, p. 1487 - 1500 (1996)

Thermal dehydration and decomposition characteristics of Fe(III) chloride hydrate have been studied by both isothermal and non-isothermal methods. After the initial melting at 35-40°C both dehydration and decomposition of the salt proceed simultaneously at temperature above 100°C. At 250-30°C a stable hydrated Fe(OH)2Cl is formed representing the first plateau region in the TG curve. Around 400°C, a second plateau is observed corresponding to the formation of mostly Fe2O3 which however retains some OH groups and Cl- ions. However, these temperature ranges vary with the TA equipments used. Chemical analysis of the products of decomposition at temperatures above 140°C also gives evidence for the formation of FeOCl which on hydrolysis in water gives FeCl3 in solution. The FT-IR spectra suggest the presence of structural OH groups even for samples calcined at 300-400°C. The XRD patterns of the products of decomposition in the temperature range 160-400°C indicate the presence of β-FeOOH, some unidentified basic chlorides and α-Fe2O3.

Synthesis, solution and spectral studies of palladium(II) complexes with 2-hydroxyacetophenone N(3)-propylthiosemicarbazone. Crystal structure of a tripalladium complex

Yadav, Paras N.,Demertzis, Mavroudis A.,Kovala-Demertzi, Dimitra,Castineiras, Alfonso,West, Douglas X.

, p. 204 - 209 (2002)

The reactions of palladium(II) salts with 2-hydroxyacetophenone N(3)-propylthiosemicarbazone, H2Ap3Pr, are described. The synthesis and spectral characterization of a new triangular, trinuclear palladium(II) complex with the dianion, Ap3Pr2-, are reported. The X-ray crystal structure determination of [Pd(Ap3Pr2)]3·DMF shows it to contain a chair-form hexagon of alternating Pd and S atoms to form a molecular bowl. The spectrophotometric characterization of H2Ap3Pr is also reported.

Steinman, R.,Schirmer, F. B.,Audrieth, L. F.

, p. 2377 - 2378 (1942)

Low-temperature structures of fac-trichloro(tetrahydrofuran)(D,L-tetrahydrofurfuranol)titanium(III) and fac-trichloro(tetrahydrofuran)(D,L-tetrahydrofurfuroxide)titanium(IV)

Olejnik, Zofia,Lis, Tadeusz,Utko, Jozef,Sobota, Piotr

, p. 847 - 850 (1996)

The title compounds, (I) [TiCl3(C5H10O2)(C4H 8O)] [IUPAC name: fac-trichloro(tetrahydrofuran)(D,L-tetrahydrofuran-2-methanol-O,O′) titanium(III)], and (II) [TiCl3(C5H

Tunable diode laser study of the reaction OH + ClO → HCl + O2

Tyndall,Kegley-Owen,Kegley-Owen,Orlando,Fried

, p. 1567 - 1575 (2002)

The main pathways for the formation of HCl in the stratosphere are through the reaction of chlorine atoms with methane and formaldehyde: Cl + CH4 → HCl + CH3. The production of HCl in the reaction of OH and ClO radicals was measured using time-resolved tunable diode laser spectroscopy. OH and ClO radicals were formed from the 308 nm laser photolysis of mixtures containing O3, Cl2, and H2O. The rate coefficient of 1.25 × 10-12 cc/molecule-sec for the reaction at 298 K was derived. This reaction rate corresponded to a branching fraction of 6.5% relative to the currently recommended rate coefficient for the overall reaction, indicating that the reaction has a significant impact on the partitioning of chlorine compounds in the stratosphere.

Kinetic study of heterogeneous reaction of deliquesced NaCl particles with gaseous HNO3 using particle-on-substrate stagnation flow reactor approach

Liu,Cain,Wang,Laskin

, p. 10026 - 10043 (2007)

Heterogeneous reaction kinetics of gaseous nitric acid with deliquesced sodium chloride particles NaCl(aq) + HNO3(g) → NaNO 3(aq) + HCl(g) were investigated with a novel particle-on-substrate stagnation flow reactor (PS-SFR) approach under conditions, including particle size, relative humidity, and reaction time, directly relevant to the atmospheric chemistry of sea salt particles. Particles deposited onto aft electron microscopy grid substrate were exposed to the reacting gas at atmospheric pressure and room temperature by impingement via a stagnation flow inside the reactor. The reactor design and choice of flow parameters were guided by computational fluid dynamics to ensure uniformity of the diffusion flux to all particles undergoing reaction. The reaction kinetics was followed by observing chloride depletion in the particles by computer-controlled scanning electron microscopy with energy-dispersive X-ray analysis (CCSEM/EDX). The validity of the current approach was examined first by conducting experiments with median dry particle diameter Dp = 0.82 μm, 80% relative humidity, particle loading densities 4 × 104 ≤ Ns ≤ 7 × 106 cm-2 and free stream HNO3 concentrations 2, 7, and 22 ppb. Upon deliquescence the droplet diameter D d approximately doubles. The apparent, pseudo-first-order rate constant determined in these experiments varied with particle loading and HNO3 concentration in a manner consistent with a diffusion-kinetic analysis reported earlier (Laskin, A.; Wang, H.; Robertson, W. H.; Cowin, J. P.; Ezell, M. J.; Finlayson-Pitts, B. J. J. Phys. Chem. A 2006, 110, 10619). The intrinsic, second-order rate constant was obtained as kII = 5.7 × 10-15 cm3 molecule-1 s-1 in the limit of zero particle loading and by assuming that the substrate is inert to HNO3. Under this loading condition the experimental, net reaction uptake coefficient was found to be γnet = 0.11 with an uncertainty factor of 3. Additional experiments examined the variations of HNO3 uptake on pure NaCl, a sea salt-like mixture of NaCl and MgCl2 (Mg-to-Cl molar ratio of 0.114) and real sea salt particles as a function of relative humidity. Results show behavior of the uptake coefficient to be similar for all three types of salt particles with Dp ~ 0.9 μm over the relative humidity range 20-80%. Gaseous HNO3 uptake coefficient peaks around a relative humidity of 55%, with γnet well over 0.2 for sea salt. Below the efflorescence relative humidity the uptake coefficient declines with decreasing RH for all three sea salt types, and it does so without exhibiting a sudden shutoff of reactivity. The uptake of HNO3 on sea salt particles was more rapid than that on the mixture of NaCl and MgCl2, and uptake on both sea salt and sea salt-like mixture was faster than on pure NaCl. The uptake of HNO3 on deliquesced, pure NaCl particles was also examined over the particle size range of 0.57 ≤ Dp ≤ 1.7 μm (1.1 ≤ Dd ≤ 3.4 μm) under a constant relative humidity of 80%. The uptake coefficient decreases monotonically with an increase in particle size. Application of a resistance model of reaction kinetics and reactant diffusion over a single particle suggests that, over the range of particle size studied, the uptake is largely controlled by gaseous reactant diffusion from the free stream to the particle surface. In addition, a combined consideration of uptake coefficients obtained in the present study and those previously reported for substantially smaller droplets (Dd ~ 0.1 μm) (Saul, T. D.; Tolocka, M. P.; Johnston, M. V. J. Phys. Chem. A 2006, 110, 7614) suggests that the peak reactivity occurs at a droplet diameter of ~0.7 μm, which is immediately below the size at which sea salt aerosols begin to notably contribute to light scattering.

Chemical vapor transport of solid solutions. 9. The chemical vapor transport of solid solutions in the system iron(II)/(cobalt(II)- and manganese(II)/cobalt(II) germanate

Pfeifer,Binnewies

, p. 1678 - 1684 (2002)

By means of chemical vapor transport methods (900 → 700°C) using HCl as transport agent FeGeO3, Fe2GeO4 and MnGeO3 have been prepared. Co2GeO4 and Fe2GeO4 as well as CoGeO3 and FeGeO3 form continuous crystalline solid solutions, whereas in MnO/CoO/GeO2 two different phases (MnxCo1-x)GeO3 are formed. All of these systems show congruent transport behaviour. Chemical vapor transport has been proved a suitable method to prepare solid solutions.

Brown,Fletcher

, p. 1223 (1950)

Bray,Dowell

, p. 905 - 905 (1917)

Pitzer

, p. 1804,1806 (1957)

Noyes, A. A.,Chow, M.

, p. 739 - 763 (1918)

-

Senter

, (1910)

-

Kinetic studies on the reactions of HCl with trans-[MoL(CNPh)(Ph2PCH2CH2PPh2) 2] (L=N2, H2 or CO)

Rosenblat, Marie-Cecile,Henderson, Richard A.

, p. 270 - 278 (2002)

The kinetics of the reactions between anhydrous HCl and trans-[MoL(CNPh)(Ph2PCH2CH2PPh2) 2] (L=CO, N2 or H2) have been studied in thf at 25.0°C. When L=CO, the product is [MoH(CO)(CNPh)(Ph2PCH2CH2PPh2) 2]+, and when L=H2 or N2 the product is trans-[MoCl(CNHPh)(Ph2PCH2CH2PPh 2)2]. Using stopped-flow spectrophotometry reveals that the protonation chemistry of trans-[MoL(CNPh)(Ph2PCH2CH2PPh2) 2] is complicated. It is proposed that in all cases protonation occurs initially at the nitrogen atom of the isonitrile ligand to form trans-[MoL(CNHPh)(Ph2PCH2CH2PPh 2)2]+. Only when L=N2 is this single protonation sufficient to labilise L to dissociation, and subsequent binding of Cl- gives trans-[MoCl(CNHPh)(Ph2PCH2CH2PPh 2)2]. At high concentrations of HCl a second protonation occurs which inhibits the substitution. It is proposed that this second proton binds to the dinitrogen ligand. When L=CO or H2, a second protonation is also observed but in these cases the second protonation is proposed to occur at the carbon atom of the aminocarbyne ligand, generating trans-[MoL(CHNHPh)(Ph2PCH2CH2PPh 2)2]2+. Addition of the second proton labilises the trans-H2 to dissociation, and subsequent rapid binding of Cl- and dissociation of a proton yields the product trans-[MoCl(CNHPh)(Ph2PCH2CH2PPh 2)2]. Dissociation of L=CO does not occur from trans-[Mo(CO)(CHNHPh)(Ph2PCH2CH2PPh 2)2]2+, but rather migration of the proton from carbon to molybdenum, and dissociation of the other proton produces [MoH(CO)(CNPh)(Ph2PCH2CH2PPh2) 2]+.

The dynamics of the Cl+n-C4H10→HCl( v′, j′) + C4H9 reaction at 0.32 eV

Bass,Brouard,Vallance,Kitsopoulos,Samartzis,Toomes

, p. 7175 - 7186 (2004)

Rotational state resolved center-of-mass angular scattering and kinetic energy release distributions were analyzed from experimental velocity-map ion images of the HCl (v′=0, j′=0-6) products of the reaction of chlorine with n-butane. It was shown that th

Braithwaite, M.,Leone, S. R.

, p. 839 - 845 (1978)

Ropp et al.

, p. 688 (1961)

Controlled synthesis of titanium dioxide nanoparticles in a modified diffusion flame reactor

Jang, Hee Dong,Kim, Seong-Kil

, p. 627 - 637 (2001)

Titanium dioxide (TiO2) nanoparticles were synthesized by the oxidation of titanium tetrachloride (TiCl4) in a modified diffusion flame reactor. The reactor utilized a multiport diffusion type burner composed of 5 concentric tubes. The flame configuration was (Ar + TiCl4)/Ar/H2/O2/air producing several tens of grams of TiO2 nanoparticles per hour. Flame characteristics of the diffusion flame at the modified burner outlet were investigated. TiCl4 concentration and flow rates of combustion gases such as oxygen, hydrogen and air were chosen as key experimental variables for the control of the particle size and phase composition. TiO2 nanoparticles ranged from 10 to 30 nm in average particle diameter, and the mass fraction of anatase synthesized was 40 to 80% in all experiments.

Synthesis of a rhenium(V) polysulfide complex and a study of its reactivity with hydrogen

Hobert, Sarah E.,Noll, Bruce C.,DuBois, M. Rakowski

, p. 1370 - 1375 (2001)

The reaction of Cp′ReCl4 (Cp′ = EtMe4C5) with 2-3 equiv of bis(trimethylsilyl)sulfide in chloroform in the presence of an oxidant results in the formation of Cp′Re(η2-S3)Cl2, 2. Complex 2 has been characterized by spectroscopic methods, and its structure has been confirmed by an X-ray diffraction study. Complex 2 reacts with hydrogen under mild conditions to form H2S, HCl, and a rhenium product tentatively identified as (Cp′Re)2S4, 3. Complex 3 reacted with benzyl bromide to form [(Cp′Re)2(μ-S2) (μ-SCH2Ph)2]Br2, 4 which has been completely characterized by spectroscopic studies and an X-ray crystal structure. The structures and reactions of the Cp′Re derivatives with sulfur ligands are compared to those of the related tetrasulfur-bridged CpMo derivatives.

Matrix isolation investigation of the photochemical reaction of activator-substituted benzenes with CrCl2O2

Hoops, Michael D.,Ault, Bruce S.

, p. 277 - 290 (2008)

The matrix isolation technique, combined with infrared spectroscopy and theoretical calculations, has been used to characterize the products of the photochemical reactions of aniline, anisole, and N,N-dimethylaniline with CrCl2O2. While initial twin jet deposition of the reagents did not lead to product formation, new bands were noted following irradiation with light of λ > 300 nm. In the reactions of CrCl2O2 and aniline, irradiation led to HCl formation, very likely accompanied by CrClO2(H)NC6H5 formation, and a mixture of isomers of CrCl2O-aminocyclohexa-2,4-dienone via oxygen atom transfer. CrCl2O2 and aniline were also codeposited as cryogenic thin films, producing new bands. Irradiation of these films led to further growth of these bands. The same products were identified in the thin film studies as were observed in the argon matrix experiments. The irradiation of the matrices containing CrCl2O2 and anisole and N,N-dimethylaniline were shown to lead to oxygen atom transfer, forming complexes between the corresponding cyclic ketone derivatives and CrCl2O. The identification of the complexes were supported by density functional calculations at the B3LYP/6-311G++(d,2p) level and isotopic labeling (in the case of aniline).

Volney

, p. 820 - 820 (1901)

Barton,Howlett

, p. 2033,2034,2035 (1951)

Photocatalytic degradation of dichloromethane by chlorocuprate(II) ions

Doyle, Kevin J.,Tran, Huy,Baldoni-Olivencia, Miguel,Karabulut, Merve,Hoggard, Patrick E.

, p. 7029 - 7034 (2008)

Near UV irradiation of aerated solutions of (Et4N) 2[CuCl4] in dichloromethane causes the decomposition of CH2Cl2, as evidenced by the buildup of HCl, C 2H2Cl4, and peroxides. A net reduction to [CuCl2]- occurs in the early stages, but is later reversed. In CH2Cl2, [CuCl4]2- is in equilibrium with [Cu2Cl6]2-, and only the latter species is photoactive. The decomposition is initiated by the photodissociation of chlorine atoms, which propagate to peroxy radicals, CHCl2OO. Experimental evidence, including a linear dependence of the decomposition rate on the incident light intensity and on the fraction of light absorbed by [Cu2Cl6]2-, is consistent with a mechanism in which CHCl2OO is reduced by electron transfer from [CuCl2]-, following which protonation yields CHCl 2OOH. The hydroperoxide accumulates during irradiation and it too can reoxidize [CuCl2]-. The quantum yield for HCl production at the outset of irradiation at 313 nm is 1.3 mol/einstein, based on the fraction of light absorbed by [Cu2Cl6]2-.

Temperature Dependence of Certain Characteristics of Hydrogen Chloride Solutions in Alcohols

Tanganov, B. B.

, p. 1101 - 1106 (2021/06/21)

Abstract: An estimate is made of the limiting values of electrical conductivity, the degree of dissociation, and the thermodynamic dissociation constants of hydrogen chloride in n-alcohols in the temperature range of 278–328?K with a step of 10?K. Multilevel modeling is used to develop model equations for estimating electrical conductivity and dissociation constants on the basis of solvents in a wide range of solution temperatures. Reliable and reproducible results are obtained with a high degree of reliability and reliability.

Biochemical Characterization, Phytotoxic Effect and Antimicrobial Activity against Some Phytopathogens of New Gemifloxacin Schiff Base Metal Complexes

Mohamed, Amira A.,Elshafie, Hazem S.,Sadeek, Sadeek A.,Camele, Ippolito

, (2021/07/26)

String of Fe(III), Cu(II), Zn(II) and Zr(IV) complexes were synthesized with tetradentateamino Schiff base ligand derived by condensation of ethylene diamine with gemifloxacin. The novel Schiff base (4E,4′E)-4,4′-(ethane-1,2-diyldiazanylylidene)bis{7-[(4Z

Investigation of kinetic parameters for ammonium perchlorate thermal decomposition in presence of gCN/CuO by TG-MS analysis and kinetic compensation correction

Jos, Jisna,Mani, Gladiya,Mathew, Suresh,Radhakrishnan Nair, P.

, (2021/06/25)

The desire to develop a benign burn rate modifier for propellants has accentuated polymeric carbon nitride (gCN) as a potential candidate for the thermal decomposition of ammonium perchlorate (AP). Here, we have synthesized composites of leaf-shaped CuO and gCN via a facile sonochemical approach. From DSC analysis, the addition of gCNCuO1 reduced the decomposition temperature of AP by 59°C and increased the heat release by ~ 1.4 times that of pure AP. The kinetics of AP decomposition was well investigated via in-situ TG-MS technique. From evolved gas analysis evolution of NO, Cl, HCl, N2O/CO2, NO2 and Cl2 fragments were detected. The quantitative interpretation of kinetic parameters for AP decomposition was done using Coats-Redfern method and the normalization of E values were carried out by applying Kinetic Compensation Correction (KCC). After normalization, E values were decreased by 17 ?kJ/mol and 18 ?kJ/mol for the first and second stages respectively.

Process route upstream and downstream products

Process route

2-chloro-4,6-diiodo-1,3,5-triazine
29633-72-5

2-chloro-4,6-diiodo-1,3,5-triazine

water
7732-18-5

water

hydrogenchloride
7647-01-0,15364-23-5

hydrogenchloride

hydrogen iodide
10034-85-2

hydrogen iodide

isocyanuric acid
108-80-5

isocyanuric acid

Conditions
Conditions Yield
at 125 ℃;
phosphorus pentachloride
10026-13-8,874483-75-7

phosphorus pentachloride

hydrogenchloride
7647-01-0,15364-23-5

hydrogenchloride

carbon dioxide
124-38-9,18923-20-1

carbon dioxide

Conditions
Conditions Yield
phenylmethanethiol
100-53-8

phenylmethanethiol

phosphorus trichloride
7719-12-2,52843-90-0

phosphorus trichloride

hydrogenchloride
7647-01-0,15364-23-5

hydrogenchloride

dibenzyl disulphide
150-60-7

dibenzyl disulphide

phosphorus pentachloride
10026-13-8,874483-75-7

phosphorus pentachloride

Conditions
Conditions Yield
at -15 - -10 ℃;
aluminium trichloride
7446-70-0

aluminium trichloride

dichloroacethyl chloride
79-36-7

dichloroacethyl chloride

hydrogenchloride
7647-01-0,15364-23-5

hydrogenchloride

2,2-dichloroacetophenone
2648-61-5

2,2-dichloroacetophenone

Conditions
Conditions Yield
P,P-dichlorophenylphosphine oxide
824-72-6

P,P-dichlorophenylphosphine oxide

water
7732-18-5

water

hydrogenchloride
7647-01-0,15364-23-5

hydrogenchloride

phenylphosphinic acid
1779-48-2

phenylphosphinic acid

Conditions
Conditions Yield
1-bromo-3-chloro-propan-2-ol
4540-44-7

1-bromo-3-chloro-propan-2-ol

hydrogenchloride
7647-01-0,15364-23-5

hydrogenchloride

hydrogen bromide
10035-10-6,12258-64-9

hydrogen bromide

Conditions
Conditions Yield
at 18 ℃; Rate constant;
at 25 ℃; Rate constant;
Ketene
463-51-4

Ketene

carbon disulfide
75-15-0,12122-00-8

carbon disulfide

aluminium trichloride
7446-70-0

aluminium trichloride

hydrogenchloride
7647-01-0,15364-23-5

hydrogenchloride

2-Methoxyacetophenone
579-74-8

2-Methoxyacetophenone

acetophenone
98-86-2

acetophenone

1-(4-methoxyphenyl)ethanone
100-06-1

1-(4-methoxyphenyl)ethanone

Conditions
Conditions Yield
at 10 ℃; und beim Erwaermen des Additionsprodukt mit Benzol und Anisol;
aluminium trichloride
7446-70-0

aluminium trichloride

bromobenzene
108-86-1,52753-63-6

bromobenzene

hydrogenchloride
7647-01-0,15364-23-5

hydrogenchloride

1.4-dibromobenzene
106-37-6

1.4-dibromobenzene

hydrogen bromide
10035-10-6,12258-64-9

hydrogen bromide

Conditions
Conditions Yield
trichloro-chloromethoxy-silane
18157-08-9

trichloro-chloromethoxy-silane

hydrogenchloride
7647-01-0,15364-23-5

hydrogenchloride

tetrachlorosilane
10026-04-7,53609-55-5

tetrachlorosilane

Conditions
Conditions Yield
beim Aufbewahren im geschlossenen Gefaess;
methoxytrichlorosilane
1825-97-4

methoxytrichlorosilane

hydrogenchloride
7647-01-0,15364-23-5

hydrogenchloride

tetrachlorosilane
10026-04-7,53609-55-5

tetrachlorosilane

Conditions
Conditions Yield

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