Transient Acid pH Effect in Tracks in The Radiolysis ofWater: Does This Effect Contribute to Biological DamageCaused by Ionizing Radiation?

Research Article

Austin J Nucl Med Radiother. 2015;2(1): 1011.

Transient Acid pH Effect in Tracks in The Radiolysis of Water: Does This Effect Contribute to Biological Damage Caused by Ionizing Radiation?

Kanike V, Meesungnoen J and Jay-Gerin JP*

Department of Nuclear Medicine and Radiobiology, University of Sherbrooke, Canada

*Corresponding author: Jay-Gerin JP, Department of Nuclear Medicine and Radiobiology, Faculty of Medicine and Health Sciences, University of Sherbrooke, 3001, 12th Avenue North, Sherbrooke, QC J1H 5N4, Canada,

Received: December 16, 2014; Accepted: February 13, 2015; Published: February 16, 2015

Abstract

We present a model calculation, using Monte Carlo track chemistry simulations, which quantitatively shows that the formation of H3O+ during the primary radiolysis processes in water renders the spur/track regions more acid than the surrounding solution. Although experimental evidence for this effect has already been reported, there is only fragmentary information on its magnitude and time dependence. Here, we compare our calculated yields of H3O+ and the corresponding pH values for both low-LET (“spherical” spur model) and high-LET (“cylindrical” track model) radiation. Our calculated time evolution of G (H3O+) in the radiolysis of pure deaerated water by 300-MeV incident protons (which mimic 60Co ?/fast electron irradiation) is in very good agreement with available experimental data. For both studied cases, an abrupt transient acid pH effect is observed at times immediately after the initial energy release. This effect, which we call an “acid spike”, is found to be greatest for times shorter than ~1ns. In this time range, the pH remains nearly constant: ~3.3 in spherical spurs and ~2.5 in cylindrical tracks. Beyond ~1ns, the pH increases gradually, ultimately reaching a value of 7 at ~1 µs for the spherical spur and at a somewhat longer time (~0.1 ms) for the cylindrical track. It does not appear that the acid spike described here has been explored in water or in a cell subject to the action of ionizing radiation. In this regard, this work raises a number of questions, some of which are briefly evoked.

Keywords: Liquid water; Aqueous solution; Radiolysis; Linear energy transfer (LET); Low- and high-LET radiation; Spur; Track; Hydrogen ion; Radiation chemical yield; pH; Biological damage; Radiobiology; Radiotherapy; Hyperthermia

Introduction

Water is the major (about 70-85%) constituent of living cells. A thorough knowledge of the radiolysis of water is therefore critical for understanding radiobiological effects. The absorption of energetic radiations by water leads to the production of reactive chemical species that can damage all biomolecules, including lipids, proteins, and DNA; DNA is considered to be the most important molecule in defining the radiobiological response. Lesions randomly induced in cellular DNA by ionizing radiation can be repaired or can result in cytotoxic and mutagenic effects and chromosomal instability, all of which can contribute to tumorigenesis [1-5].

It has been customary to separate the complex succession of events that follow the irradiation of water into four, more or less clearly delineated, consecutive, temporal stages [6-9]. Briefly, the first or “physical” stage consists of the phenomena by which energy is transferred from the incident radiation to the water. Its duration is of the order of 10-16 s or less. This energy absorption gives rise, along and around the path of the radiation, to a large number of ionized (H2O•+) and electronically excited (H2O* elec) water molecules distributed in a specific, highly non-homogeneous track structure which depends on the type and energy of the radiation used. Secondary electrons generated in the ionization events have a wide range of energies. Generally, they have enough energy to ionize or excite one or more other water molecules in the vicinity. The second or “physicochemical” stage consists of the re-establishment of thermal equilibrium in the bulk medium with reactions and the reorganization of initial products to give new chemical species such as stable molecules and water free radicals. It lasts about 10-12 s. During this stage, secondary electrons slow down to thermal energy (eth ) and, following thermalization, they become trapped (etr ) and hydrated (e-aq). By ~10-12 s, the radiolysis of water can be simply described by the following reactions [8,9].

H2O H2O+

+ e- (1)

H2O H2O*elec (2)

H2O+ + H2O ? H3O+ + •OH (3)

e- → e- th → e- tr → e- aq (4)

H2O* elec → H• + •OH (5)

where H3O+ (or equivalently, Haq +) represents the hydrated proton. In addition to the two radical species e- aq and •OH (hydroxyl radical), a small quantity of H• atoms and the molecular products H2 and H2O2 are produced. The third or “chemical” stage consists of diffusion and reactions of the reactive species leading to the re- establishment of chemical equilibrium. During this stage, the various radiolytic products present at the end of the physicochemical stage diffuse away from the site where they were originally produced and then either reacts within the tracks as they develop in time or escape into the bulk solution. At 25 °C, all intra-track reactions are essentially complete by ~10-6 s after the initial energy deposition. At this time, the species that have escaped from track reactions become homogeneously distributed throughout the bulk of the solution (also referred to as the “background”) and the radiation track no longer exists. The radical and molecular products, considered as additions to the background, are then available for reaction with dissolved solutes (if any) present (in moderate concentrations) at the time of irradiation. On a quantitative basis, the species produced in the radiolysis of pure deaerated (air-free) water at homogeneity are e- aq, H3O+, H•, •OH, OH-, H2, H2O2, O2 •- [or its protonated form HO2 •, depending on the pH; pKa (HO2 •/O2 •-) = 4.8 in water at 25 °C], etc. In air-saturated solutions (the concentration of oxygen is ~0.25 mM), e- aq and H• atoms are rapidly (on a time scale of a few tenths of a microsecond) converted to superoxide anion/hydroperoxyl radicals. Thus, in an aerobic cellular environment at pH 7, the major reactive species at homogeneity include O2 •-, •OH, and H2O2 (H2 plays only a limited role in the radiolysis of aqueous solutions, and most of it escapes from solution). Finally, in a physiological system, there follows a “biological” stage in which the cells respond to the damage resulting from the products formed in the preceding stages (~10-3 s or longer, depending very much upon the medium). A good summary of the present status of aqueous radiation chemistry is given in [9-13].

Many experimental and theoretical studies have shown that the yields in the radiolysis of water are strong functions of the quality of the incident radiation, a measure of which is given by the “Linear Energy Transfer” (LET) (also called “stopping power” by physicists) that represents the non homogeneity of the energy deposition on a sub-microscopic scale, commonly referred to as the “track structure” [8,9,14]. (Throughout this article, radiation chemical yields are given as G-values, in units of radicals, ions or molecules per 100 eV of energy deposited; for conversion into SI units, 1 molecule/100 eV ≈ 0.10364 μmol/J.) At the lowest LET (e.g., for sparsely ionizing radiation such as γ-rays from 60Co, fast electrons or ~300 MeV protons generated by a particle accelerator, LET ~ 0.3 keV/μm), tracks are formed initially by well-separated Magee-type “spurs” [15,16] (spherical in shape) that develop independently in time (without interference from the neighbouring spurs). In this case, the predominant effect is radical production. As LET increases, the mean separation distance between the spurs decreases and the isolated spur structure changes to a situation in which the spurs overlap and form a dense continuous column (cylinder shape). This permits more radicals to be formed in close proximity with correspondingly greater probability of reacting with one another to produce molecular products or to reform water. High-LET, densely ionizing radiation therefore tends to produce high yields of molecular products, at the expense of free-radical yields [9,17]. To illustrate this point, {Figure 1} shows typical twodimensional representations of the track segments of 300- and 0.15- MeV irradiating protons (LET ~ 0.3 and 70 keV/μm, respectively) on liquid water at 25 °C, calculated with our IONLYS Monte Carlo simulation code {Figure 1}.