1. Introduction
The generally accepted term “sulfite” identifies sulfiting agents such as sulphur dioxide gas, metabisulfite, bisulfite and sulfite. These are all widely used in food and beverage preservation for their antioxidant properties [1] [2] , in commercial goods and pharmaceuticals as antimicrobial agents, and also present as pollutants in the atmosphere. Endogenously generated during the normal metabolic processing of sulfur-containing amino acids or drugs, bisulfite level in the body is tightly regulated by the sulfite-oxidase that acts as detoxifier for endogenous and exogenous sulfite [3] . An extreme example of the necessity of having the concentration of sulfite under tightened control is a congenital disease, the sulfite-oxidase deficiency, which causes an increase in sulfite concentration, and individuals suffering from this genetic disorder develop severe neurological abnormalities leading to an early death [3] . Sulfite has also been suggested as an endogenous mediator in host defense and/or inflammation, as it activates human neutrophils, in vitro, which is one of the key events in the pathogenesis of endotoxemia and, indeed, more generally of the inflammatory response. In healthy individuals beside enzymatic transformation other processes to control the level of sulfite must be involved: for instance, chemical pathways. In fact, the sulfite reacts with disulfide proteins bond such as oxidized glutathione and cystine leading to the formation of the corresponding sulfidryl derivative, or is oxidized to sulfate [4] [5] . But, the mechanism of both the negative and positive actions in which the sulfite could be involved is not clear; for example, it has been suggested that the sulfite might affect some mediators such as the nitric oxide and/or its carriers [6] -[8] . Actually, the sulfite might act as a cofactor of NO releasers [6] -[12] . However, the only evidence reported in favor of this possible synergy has been the highlighting of a decrease in concentration of the S-nitrosoglutathione in the interaction with the bisulfite, as detected by UV spectroscopy [6] , and the potential depletion of the extracellular pools of S-nitrosothiol compounds [7] is never fully supported [13] [14] . Furthermore, as for other gasotransmitters, this hypothesized interaction seems to take place mainly in acidic condition [15] (Scheme 1).
2. Experimental
2.1. Materials
All experiments were conducted at room temperature with commercial products except GSNO, S-nitrosoglutathione, which was synthesized as reported in the literature [16] , and the Fe2+(DETC)2, iron (II) N, N-diethyldithiocarbamate, which was synthesized as follows: 25 mL of a water solution of diethyldithiocarbamate (DETC), 20 mmol/L, were added to 100 mL of a water solution of FeSO4∙7H2O, 10 mmol/L, over a 60-min period. The mixture was stirred for two hours and the precipitate, Fe2+(DETC)2, collected by filtration, washed several times with water, and dried under vacuum; all processes were conducted in a rigorous nitrogen atmosphere.
2.2. Trapping of NO
To compare the efficiency of the processes a quantitation of the NO released, via quantitative measurements of NO-Fe(DETC)2, was conducted according to the following procedure.
After running the EPR-analysis of the samples, the measurement of an internal paramagnetic standard, a synthetic ruby-crystal not removable located inside the spectrometer’s cavity, was carried out; in particular, the measurement was conducted without removing the sample-tube (the same for all the experiments), and using the same instrumental setup. Afterwards, the spectrum of a 10−5 M benzene solution of DPPH (1,1-diphenyl-2-picrylhydrazyl radical), a spin-concentration reference, was recorded, followed by the measurement of the internal paramagnetic standard. All signals, before to be analyzed, were computing double integrated. Since the intensity of the ruby signal cannot change, the ratio of the double integrals provides a correction factor for the different sensitivity of the cavity for each sample. Thus, the comparison of the intensity of the signals of the NO samples with that obtained from the DPPH, after the sensitivity correction, allows determining the radical concentration in the examined samples. In particular, the absolute concentration of NO for the experiments with NaNO2/ NaHSO3 and GSNO/NaHSO3 resulted 5.07 × 10−6 M and 1.41 × 10−6 M, respectively. For the blank GSNO experiment the absolute concentration of NO was determined to be 2.19 × 10−7 M. The amount of NO detected comes from an experiment of the duration of 10 minutes, and therefore do not represent the total amount that in principle could be obtained by collecting NO up to depletion of the reaction. The purpose was just to obtain quantitative values of NO, thus to be able to compare of efficiency in nitric oxide releasing from two different NO-releasers present in vivo.
3. Results and Discussion
Since the GSNO/bisulfite interaction was hypothesized [7] , to prove or disclaim this as a way of production of NO, a blank experiment with GS-NO, in buffer solution (pH = 6.4), was carried out, (Scheme 2(a)).
The EPR analysis of the resulting trap-solution highlights the formation of the paramagnetic adduct NOFe(DETC)2, in low amount (Figure 1 red trace), due to the thermo-induced release of NO [13] , as well as the fading of the characteristic pink color of the solution due to the decrease of the GS-NO concentration, which

Scheme 1.Schematic illustration reflecting the interaction between bisulfite and nitrite.
(a)
(b)
Scheme 2.Spin-trapping of NO released by GSNO in buffer solution at pH = 6.4: (a) via homolytic cleavage; (b) induced by bisulfite.

Figure 1. EPR spectrum of NO-Fe(DETC)2, aN = 1.28 mT and g = 2.039 red trace―NO released via the thermal induced homolysis of GSNO; green trace―NO released in the reaction between GSNO and the bisulfite; blue trace―NO released in the reaction between NaNO2 and the bisulfite. It must be noted that in the experimental spectra the Magnetic Field is listed in Gauss (G), whilst the value reported in the text is in mT, (1 mT = 10 G), as requested by SI. Finally, the spectra are experimental and worked (color and double integration) using Excel.
even if qualitative can be considered a positive supporting proof. However, since the possible role of the bisulfite as a cofactor of NO-derivatives was not clearly demonstrated, a test with GSNO and NaHSO3, in buffer solution (pH = 6.4), was conducted.
This time, the spin-trap solution showed an intense EPR signal of the trapped radical, NO-Fe(DETC)2 (Figure 1 green trace), and a rapid, intense bleaching of the pink-colored solution. These proofs led to hypothesize the possibility to induce nitric oxide release via interaction with the bisulfite also from other NO releasers. In this light, the nitrite, claimed as the most important reservoir of NO in vivo [17] , was tested. The experiment, conducted in acidic buffer solution (pH = 6.4), allowed the detection of a very intense EPR signal due to the NO-Fe(DETC)2, (Figure 1 blue trace), which proved the abundant release of NO, and the high efficiency of the process [12] .
Although this was a strong evidence of the positive interaction bisulfite/nitrite, frequently the dismutation of the nitrous acid is invoked as responsible of NO production in acid medium, so a blank test with nitrite in acidic buffer solution, pH = 6.4, was conducted. The possible NO formed was collected for more than 40 minutes (four times the collecting time used for the experiments with the bisulfite!), and the spin trap solution analyzed. The EPR spectrum showed a very feeble signal of the NO-Fe(DETC)2 adduct, fully negligible compared to that obtained in the experiment conducted in the presence of the bisulfite, leading to conclude that the hypothesized production of NO via dismutation is totally irrelevant.
Among the physiological roles of the sulfite, the interaction with NO gas was also hypothesized [8] , but this possibility has to be excluded since the chemistry of NO allows reactions only with radical species, or the coordination to metal ions. Most probably, to account for the results reported in the literature [8] [19] , different intermediates, or reactions, leading to a sulfite-derived radical must be hypothesized.
The evidences obtained in the GSNO blank experiment could support the thermal homolysis of S-nitrosothiols (S-N bond), as responsible for the NO release [13] , and then the involvement of the bisulfite in principal unnecessary, Scheme 1(a); on the contrary, those obtained from the reaction between GSNO and the bisulfite were unquestionably opposite. In fact, the fast and marked fading of the solution (pink color), and the intense EPR-signal of the NO-Fe(DETC)2, proved the involvement of the bisulfite, Scheme 2(b). As a matter of fact, the very low rate of the S-N bond homolysis in these experimental conditions would not be able to account for this result [13] , Scheme 2(a). Furthermore, the quantitation of NO, Figure 2, shows that the amount of NO-Fe(DETC)2 radical detectable is 6.44 times higher when GSNO is reacted with the bisulfite compared to the blank experiment.
However, since S-nitrothiols do not represent the main reservoir of NO in vivo but, as widely accepted is the nitrite [17] [18] , its possible interaction with the sulfite would be truly significant and could disclose a new scenario [20] [21] . For example, because the level of the sulfite must be closely regulated in the body, its interaction with the nitrite could contribute to keep the sulfite under control (lowering the concentration!) through a chemical pathway, as well as to support the hypothesized function of the nitrite as the mediator of the sulfite action [6] [12] , Scheme 3.
The result obtained in the presence of the nitrite, analogously to that reported for the hydrogen sulfide [15] , show a process under pH control, i.e., the NO release is more efficient in acidic medium. Actually, these conditions might correspond, in vivo, to those in which the synergy between the sulfite and NO transporters is invoked;

Figure 2. Quantitative comparison (NO) of the EPR spectra obtained from the reaction between the GSNO and the bisulfite, and the GSNO alone.

Scheme 3. NO release induced by the bisulfite on the nitrous acid at pH = 6.40.

Figure 3. Quantitative comparison (NO) of the EPR spectra obtained from the reaction between the Nitrite and the bisulfite (blue), and GSNO and the bisulfite (green).
for example, patients in acute phase of inflammation that show high acidity and high levels of serum sulfite [10] [11] . Thus, pH-sensitive NO derivatives must be taken into consideration: the nitrite, whose aci-form (HO-NO) increases in acidic condition, fulfills this request, since able to undergo a reductive NO release, Scheme 2.
The focal role of the interaction between the nitrite and the bisulfite, as a source of NO, is definitely supported by the quantitation of nitric oxide released: it results 3.61 times higher than that released in the interaction with GSNO, Figure 3.
4. Conclusion
In the light of these results, as for molecules hypothesized to have a gasotransmitter role [14] , the bisulfite also requires synergy with NO releasers to account for its actions, and such behavior leads to underline the role of the bisulfite as a cofactor. Moreover, it is worth noting that the nitrite plays a crucial role regarding all species considered gasotransmitters, and therefore a more careful study of its “chemistry” in vivo would be fundamental also for understanding the positive and/or negative effects of molecules such as the sulfite.
Acknowledgements
This work was financially supported by MIUR, Rome, Fund PRIN 2010-2011 2010PFLRJR (PROxi project). I thank L.A. Winter for the helpful discussion.