Photolysis of hydrazoic acid in aqueous solution

Photoinduced C−N Bond Cleavage in 2-Azido-1,3-diphenyl-propan-1-one Derivatives: Photorelease of Hydrazoic Acid

Photolysis of 3-azido-1,3-diphenyl-propan-1-one (1a) in toluene yields 1,3-diphenyl-propen-1-one (2), whereas irradiation of 3-azido-2,2-dimethyl-1,3-diphenyl-propan-1-one (1b) results in the formation of mainly 2,2-dimethyl-1,3-diphenyl-propan-1-one. Laser flash photolysis (308 nm) of 1a,b in acetonitrile reveals a transient absorption (lambda max = approximately 310 nm) due to the formation of radicals 4a and 4b, respectively, which have lifetimes of approximately 14 micros at ambient temperature. TD-DFT calculations (B3LYP/6-31+G(d)) reveal that the first and second excited states of the triplet ketone (T1K (n,pi*) and T2K (pi,pi*)) in azide 1a are almost degenerate, at approximately 74 and 76 kcal/mol above the ground state (S0), respectively. Similarly, azide 1b has T1K and T2K 75 and 82 kcal/mol above S0, respectively. The calculated transition state for cleaving the C-N bond is located 71 and 74 kcal/mol above S0 in azides 1a and 1b, respectively. The calculated bond dissociation energies for breaking the C-N bond are 55 and 58 kcal/mol for azides 1a and 1b, respectively, making C-N bond breakage accessible from T1K in azides 1 at ambient temperature. In comparison, the irradiation of azides 1 in argon matrices at 14 K lead to the formation of the corresponding triplet alkyl nitrenes (1-n), via intramolecular energy transfer from T2K. The characterization of 1-n was supported by isotope labeling, IR spectroscopy, and molecular modeling.

Physical, chemical and environmental properties of selected chemical alternatives for the pre-plant use of methyl bromide as soil fumigant

Production and use of methyl bromide, a soil fumigant, are being restricted because of this chemical's deleterious effects on stratospheric ozone concentrations. Several products, some of which are currently used as soil fumigants, are being considered as possible replacements for methyl bromide, alone and in various combinations. Among these, 1,3-dichloropropene, methyl isothiocyanate generators such as metam-sodium, and chloropicrin are currently registered, while others such as methyl iodide and sodium azide are at different stages of the registration process. This review examines physicochemical properties, environmental fate, and metabolism of the various potential methyl bromide replacement products.

Atmospheric chemistry of hydrazoic acid (HN3): UV absorption spectrum, HO reaction rate, and reactions of the N3 radical

Processes related to the tropospheric lifetime and fate of hydrazoic acid, HN3, have been studied. The ultraviolet absorption spectrum of HN3 is shown to possess a maximum near 262 nm with a tail extending to at least 360 nm. The photolysis quantum yield for HN3 is shown to be approximately 1 at 351 nm. Using the measured spectrum and assuming unity quantum yield throughout the actinic region, a diurnally averaged photolysis lifetime near the earth's surface of 2-3 days is estimated. Using a relative rate method, the rate coefficient for reaction of HO with HN3 was found to be (3.9 +/-0.8) x 10(-12) cm3 molecule(-1) s(-1), substantially larger than the only previous measurement. The atmospheric HN3 lifetime with respect to HO oxidation is thus about 2-3 days, assuming a diurnally averaged [HO] of 10(6) molecule cm(-3). Reactions of N3, the product of the reaction of HO with HN3, were studied in an environmental chamber using an FTIR spectrometer for end-product analysis. The N3 radical reacts efficiently with NO, producing N2O with 100% yield. Reaction of N3 with NO2 appears to generate both NO and N2O, although the rate coefficient for this reaction is slower than that for reaction with NO. No evidence for reaction of N3 with CO was observed, in contrast to previous literature data. Reaction of N3 with O2 was found to be extremely slow, k < 6 x 10(-20) cm3 molecule(-1) s(-1), although this upper limit does not necessarily rule out its occurrence in the atmosphere. Finally, the rate coefficient for reaction of Cl with HN3 was measured using a relative rate method, k = (1.0+/-0.2) x 10(-12) cm3 molecule(-1) s(-1).

Toxicology of selected nitric oxide-donating xenobiotics, with particular reference to azide

Nitric oxide (NO) has been discovered recently to be a ubiquitous, endogenous mediator, which is responsible for a variety of normal physiological functions. However, NO also has been implicated in several pathophysiological processes. For example, the pulmonary toxicity of various nitrogen oxides, including NO, found in photochemical smog has been studied for decades; endogenous NO also is associated with bleomycin-induced lung damage, as well as other adverse effects. Recently, a variety of xenobiotics have been shown to owe their biological activity in vivo to their biotransformation to NO. Thus, the therapeutic vasodilatation produced by drugs such as nitroglycerin and sodium nitroprusside is now believed to result from their release of NO, which then mimics the effects of endogenously synthesized NO. The toxic effects of NO prodrugs are, therefore, a matter of concern, especially the extent to which, if any, NO contributes to their toxicity. As reviewed here, NO does not appear to contribute importantly to the toxicity of the NO donors nitrite, hydroxylamine, or nitroprusside. However, it is by no means clear whether or not the NO generated in vivo from sodium azide contributes in a major way to its toxicity. Azide is almost as acutely toxic as cyanide, with which it shares a number of biological effects; yet, azide also has certain cardiovascular actions in common with nitrite. Unlike either cyanide or nitrite, some evidence suggests a tendency for azide to produce low-grade cumulative toxicity. In laboratory animals, azide frequently produces nonasphyxial convulsions, whereas most human deaths appear to be the result of cardiovascular collapse. Neither of these azide-induced syndromes appears to be due to the inhibition of cytochrome c oxidase. Azide is widely used as a preservative in aqueous laboratory reagents and as the propellant in automobile air bags and aircraft escape chutes. Both of these inflable systems are generally safe, and will prevent untold numbers of injuries and deaths. However, to protect workers who handle these devices and others who may come into contact with the sodium azide propellant in these systems, our rudimentary knowledge of azide toxicity needs to be expanded.