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. Author manuscript; available in PMC: 2013 Nov 15.
Published in final edited form as: Free Radic Biol Med. 2012 Aug 22;53(10):1968–1976. doi: 10.1016/j.freeradbiomed.2012.08.013

Glutathiyl Radical as an Intermediate in the Glutathione Nitrosation*

Kumpal Madrasi 1, Mahesh S Joshi 1,a, Tushar Gadkari 1, Konstantinos Kavallieratos 2, Nikolaos M Tsoukias 1
PMCID: PMC3494776  NIHMSID: NIHMS402536  PMID: 22951977

Abstract

Nitrosation of thiols is thought to be mediated by Dinitrogen Trioxide (N2O3) or by Nitrogen Dioxide radical (NO2). A kinetic study of Glutathione (GSH) nitrosation by NO donors in aerated buffered solutions was undertaken. S-nitrosoglutathione (GSNO) formation was assessed spectrophotometrically and by chemiluminescence. Results suggest an increase in the rate of GSNO formation with an increase in GSH with a half-maximum constant EC50 that depends on NO concentration. Our observed increase in EC50 with NO concentration suggests a significant contribution of NO2 mediated nitrosation with the glutathiyl radical as an intermediate in the production of GSNO.

Keywords: Glutathione, nitric oxide, thiyl radical, kinetics

Introduction

Blood vessel dilation [1], signal conduction in nervous system [2], and cytotoxic activity against microbes [3] are amongst the important physiological roles played by NO. For free NO to perform these functions, it should be able to reach its sites of action without being scavenged through its reaction with heme proteins[4]. Formation of nitrosothiols can increase the half – life of NO in the vasculature and thus can enhance its biological functions. The formation of β–93 cysteine nitrosothiols on the hemoglobin molecule [5]and the combination of NO with low molecular weight thiols are two candidate pathways for NO preservation[6]. Nitrosothiols have been found to be potent vasodilators and inhibitors of platelet aggregation and may also play important roles in signaling pathways. In view of the importance of nitrosothiols in biological systems, it is of interest to elucidate the kinetic mechanism and assess the rate of their formation. Of particular interest is the nitrosation of glutathione due to its abundance in biological tissues [38]. Glutathione nitrosation has been proposed to occur via an initial reaction of NO with O2 and the subsequent formation of N2O3, which acts as the nitrosating agent for GSH. The suggested reaction mechanism for this route of nitrosation is as follows [7,17, 33, 36]:

2NO+O2k12NO2 Reaction 1
NO2+NOk-2k2N2O3 Reaction 2
GSH+N2O3k3GSNO+NO2-+H+ Reaction 3
N2O3+H2Ok42NO2-+2H+ Reaction 4

Recent evidence shows that in adequately oxygenated solutions the NO2 can oxidize the GSH to form the glutathiyl radical (GS) which reacts with NO to form GSNO [8, 16, 22, 39]. This scheme would include the same rate limiting step (Reaction 1) as well as Reactions 2 and 4. However, nitrosation would proceed through Reactions 5 and 6 instead of 3.

N·O2+GSHk5GS·+NO2- Reaction 5
GS·+N·Ok6GSNO Reaction 6

Thus, according to the second kinetic mechanism the NO2 can react with GSH to give GSNO (Reaction 5), but also reacts with NO to form N2O3 (Reaction 2). This cross talk between the two alternative pathways poses a significant obstacle in determining the relative contribution of the two mechanisms. Thus, despite recent evidence that propose NO2 as the active intermediate for nitrosation [8, 16, 22, 39], the importance of N2O3 vs NO2 in thiol nitrosation has not been conclusively determined [7, 17, 33, 36]. In this study, we have followed the kinetics of the GSH nitrosation reaction in an attempt to elucidate the reaction mechanism and to identify the role of N2O3 and NO2 as nitrosating intermediates.

Recent data [22] has documented significant GSSG formation during the nitrosation of GSH by NO donors, which involves the formation of the thiyl radical. This essentially validates the second reaction mechanism above, since the presence of GSSG means that there has been formation of the glutathiyl radical (GS). One potential route of GSSG formation is through the following series of reactions:

GSHk-7k7GS-+H+ Reaction 7
GS·+GS-k-8k8GSSG- Reaction 8
GSSG-+O2k9GSSG+O2·- Reaction 9

Alternatively, GSSG can be formed from GSNO according to Reaction 10 [50].

GS·+GSNOk10GSSG+N·O Reaction 10

The proposed, simplified kinetic mechanisms do not consider a number of relevant reactions including alternative reactions for GSSG formation as well other reactions that are involved in GSH and NO oxidation chemistry. In the Supplement, we present a mathematical model of 25 relevant reactions and we compare model predictions for GSNO formation rate against the output of the two simplified reaction schemes.

Materials and Methods

Materials

Glutathione (GSH), N-Ethyl Maleimide (NEM), and Diethylene Triamine Pentaacetic Acid (DTPA) were obtained from Sigma Aldrich Co (St. Louis, MO). NO donors Propylamine Propylamine NONOate and Diethylamine NONOate (PAPA/NO and DEA/NO) and S-nitrosoglutathione were obtained from Cayman Chemical Co (Ann Arbor, MI).

NO release by NO donor

NO donors were chosen with an appropriate half – life; a suitably long half – life confers on them the ability to generate steady NO levels over the duration of the experiment (see results section). At 20–25°C PAPA/NO and DEA/NO have a half – life of approximately 77 min and 16 min respectively. To validate theoretical predictions for the pattern of NO release from NO donors, we used different concentrations of PAPA/NO ranging from 500 μM to 10 mM in a pH of 7.4 and measured NO release using a commercially available NO-sensitive electrode (WPI, Sarasota, FL).

GSNO measurements

UV-visible spectro-photometry was carried out by a Cary 100 Bio UV-Vis spectrophotometer. GSH concentrations ranged from 200 μM to 5mM and PAPA/NO concentrations from 500 μM to 10 mM. Reactions were carried out in 1 mL size quartz cuvettes as in Fields et al. [9]. GSNO formation in a mixture of GSH and PAPA/NO was followed at 338 nm (molar absorptivity of 900 M−1cm−1) [10]. We also measured GSNO formed using chemiluminescence analysis. The Copper (I) Chloride and Cysteine (2C) assay method was used to measure GSNO through a chemiluminescence analyzer (Sievers 280i NOA) as described in earlier works [11,12,24, 73]. Different GSH concentrations (200 μM to 7.5 mM) and DEA/NO (31.25 μM to 500 μM) were incubated in Eppendorf tubes. Reactions were stopped with 10 mM NEM at 2, 3 and 4 minutes. The solutions were left at room temperature in the dark for about an hour for the NO donor to completely decay, so as to avoid any NO signal in the assay from the NO donor. Following this period, GSNO content in our samples was analyzed. All reactions followed by spectrophotometry or by chemiluminescence were performed in 40 mM phosphate buffer (pH = 7.4) supplemented by 50 μM DTPA at 20–25 °C. To check for interference from other NO-derived species, samples were incubated with 2.5 mM HgCl2 for half an hour to abolish GSNO content [13] prior to the 2C assay.

“Clamped NO” protocol

A combination of an NO donor and an NO scavenger (i.e. CPTIO) has been previously utilized to maintain steady levels of NO in solution (i.e. “clamped NO protocol” [59]). We hypothesized that a similar “clamped NO” condition can be achieved in aerated solutions of NO donors where O2 will be the predominant NO scavenger. Thus, a relative steady NO concentration is expected as a result of the balance between NO release by the donor and consumption by the oxygen content of the solution. We also refer to this as the “clamped NO concentration” similar to Griffith et al.[59].

Assuming that every mole of NO donor releases n moles of NO, the NO release rate by the NO donor is given by Eq. 1a.

S=nkd[NOdonor]e-kdt Eq. (1a)

where kd = ln(2)/t1/2 and t1/2 is the half – life of the NO donor. For times less than 1/10 of the half – life of the NO donor the release rate remains relatively constant and can be approximated by:

S=nkd[NOdonor] Eq. (1b)

In the absence of other NO scavengers NO is consumed through the reaction with dissolved O2 (Reaction 1) and through Reaction 2. Reaction 1 is the rate-limiting reaction and thus total NO consumption can be approximated by:

R=4k1[O2][NO]2 Eq. (1c)

At equilibrium, the balance between Eq. 1b and Eq. 1c yields a steady NO level:

[NO]=nkd4k1[O2][NOdonor] Eq. (1d)

Thus, NO levels should remain relatively constant and concentrations should increase proportionally to the square root of the NO donor concentration.

Pseudo steady state approximation

A pseudo steady state approximation has been previously employed by Kharitonov et al. to simplify the kinetic mechanism (Reactions 14) [17]. Assuming small concentration of unstable intermediates NO2, N2O3 and thus negligible rates of change for these complexes we get:

d[GSNO]dt=2k1[NO]2[O2][GSH][GSH]+k4k3 Eq. (2a)

On the other hand, the pseudo steady state approximation for the Reactions 1, 2, 4, 5, and 6 gives us the rate of nitrosation as:

d[GSNO]dt=2k1[NO]2[O2][GSH][GSH]+k2k4[NO][k-2+k4]k5 Eq. (2b)

Note that Eq. 2b in agreement with Eq. 2a suggests saturation kinetics with respect to the concentration of GSH. In Eq. 2b, however, the half-maximum constant EC50 is dependent on the NO concentration. Thus, an effective EC50 value equal to k2k4[NO][k-2+k4]k5 is predicted. Experimentation will test the saturation kinetics of this rate law. Thus the rate of GSNO formation will be equal to the product of the maximum rate at saturating concentrations (Vmax = 2k1[NO]2[O2]) times a factor m that differs between the two proposed mechanisms. According to the first mechanism (Eq. 2a), m1=k3[GSH]k3[GSH]+k4 while based on Eq. 2b, m2=k5[GSH]k5[GSH]+k2k4[NO](k-2+k4). Eq. 2a and 2b simply state that the rate is limited by the rate of NO oxidation (Reaction 1) and the fraction of N2O3 or NO2 utilized in GSH nitrosation ( m1=Rxn3Rxn3+Rxn4,m2=Rxn5Rxn5+Rxn2). The functional difference between the two mechanisms arise from the NO dependency in the scavenging of the active intermediate in mechanism 2 (i.e. NO2 scavenging through Reaction 2) vs the NO-independent consumption of the active intermediate in mechanism 1 (i.e. N2O3 scavenging through Reaction 4). Based on Eq. 2b, EC50 will increase with NO concentration, if NO2 is the major nitrosating intermediate. On the other hand, based on Eq. 2a, an EC50 value that remains relative steady at different levels of NO, is indicative of N2O3 as the nitrosating intermediate.

When we incorporate Reactions 79 into kinetic mechanism 2 to account for the formation of GSSG, PSSA yields:

d[GSNO]dt=2k1[NO]2[O2][GSH][GSH]+k2k4[k-2+k4]k5[NO]×k6[NO]k6[NO]+k8k7k-7[GSH] Eq. (2c)

The difference between Eq. 2c and 2b is a correction factor f=k6[NO]k6[NO]+k8k7k-7[GSH] that accounts for the fraction of total GS utilized in the formation of GSNO (i.e. f=Rxn6Rxn6+Rxn8). Eq. 2c reduces to Eq. 2b when [NO][GSH]k8k7k6k-7. Incorporating Reaction 710 to the simplified kinetic mechanism 2 and applying PSSA yields:

d[GSNO]dt=2k1[NO]2[O2][GSH][GSH]+k4k2[NO][k-2+k4]k5×k6[NO]-k10[GSNO]k6[NO]+k8k7[GSH]k-7+k10[GSNO] Eq. (2d)

For low GSNO levels (i.e. [GSNO]k6k10[NO]) Eq. 2d reduces to Eq 2c, thus Reaction 10 should not affect initial formation rates. However, Eq. 2d suggests that in a “clamped NO” condition, GSNO accumulation will lead to an equilibrium point with steady GSNO levels i.e. [GSNO]=k6k10[NO].

Results

Dependence of [NO] on [NO donor]

First, we investigated the pattern of NO release by NO donors to confirm our theoretical predictions (Eq. 1d). NO release was measured with varying concentrations of PAPA/NO (500 μM to 10 mM) electrochemically using an NO electrode. A sample reading is shown in Fig. 1A. As NO release occurs, concentration levels rise to a peak value before reaching a slowly decaying plateau. As expected, decay in NO concentration occurs as a result of NO donor consumption over time. The long half – life of the NO donor allows for a relative steady level of NO over an adequate time frame. Peak NO concentrations from NO recordings at different NO donor concentrations were used to generate a log − log graph of [NO] vs. [PAPA/NO] (n=4). The result is shown in Fig. 1B. The linear relationship between log[NO] and log[PAPA/NO] has a slope of 0.51 ± 0.04 and it is not statistically different from 1/2(p =0.30). As expected, based on Eq. 1d, established NO levels are proportional to the square root of the utilized NO donor concentration, i.e. [NO][NOdonor].

FIGURE 1.

FIGURE 1

(A) Release of NO from PAPA/NO (500 μM). NO concentration is monitored with a NO-sensitive electrode for 30 min. After an initial accumulation period, NO levels remain relative steady for a significant time period. (B) log-log graph showing relation between maximum NO concentrations achieved at different PAPA/NO concentrations (n = 4). The slope of 0.51 ± 0.04 is not statistically different from 0.5 (p = 0.30).

Electrode data thus yield the following linear relationship between clamped [NO] and [PAPA/NO]

[NO]=0.23±0.02[PAPA/NO] Eq. (3)

This result would be in agreement with Eq. 1d for n×kd= 1.58±0.03 ×10−4s−1 for PAPA/NO under the conditions of our experiment. [Reported stoichiometry (n=2) and half – life(t1/2= 77 minutes) [14, 15] for PAPA/NO at room temperature yield n×kd=3 × 10−4 s−1 but these values may change with experimental conditions [60, 61]]. We use Eq. 3 to better predict [NO] for every [PAPA/NO] in further analysis rather than using Eq. 1d with the reported half – life of PAPA/NO.

Dependence of EC50 on [NO]

Fig. 2A shows a representative recording of GSNO formation in the spectrophotometer for a particular GSH (250 μM) and NO donor concentration (PAPA/NO; 1mM). Recordings show a relative constant rate of GSNO formation over a period of a few minutes. The slope of this tracing where NO concentration would have peaked was recorded (red circle in Fig. 2A) and corresponds to the maximum rate of GSH nitrosation at the particular NO donor and GSH concentration. The use of this slope rather than initial slope is necessitated to account for the time required for NO to evolve. We ensure that peak/plateau NO concentration is reached fast after mixing with GSH and thus GSH concentration has not changed significantly from initial time and formation of GSNO is low (i.e. [GSNO]k6k10[NO]). Experiments were repeated for different GSH concentrations at each NO donor concentration and the results are summarized in Fig. 2B for three PAPA/NO concentrations (500 μM, 1 mM and 5 mM). In the inset, Vmax/V vs. 1/GSH plots were made (‘V’ indicates the rate of nitrosation). Linear least square fittings followed by taking the slope yields EC50 values at each NO donor concentration. We observe a NO concentration dependent shift in EC50 values. As the NO donor concentration increases the EC50 value also increases.

FIGURE 2.

FIGURE 2

(A) Representative data for GSNO formation as a function of time. GSNO concentration was monitored in a spectrophotometer at 338 nm, following mixing of GSH (250 μM) and PAPA/NO (1 mM). Data were fitted by a 5th order polynomial to remove noise (dashed black line). The maximum slope of the polynomial is identified (red circle) and corresponds to the GSNO formation rate at peak NO concentration. (B) Rates of nitrosation (V) at three different NO donor concentrations (500 μM (red), 1 mM (blue) and 5 mM (green)) are plotted against GSH concentrations. Inset shows Vmax/V plotted against 1/GSH. Slope of these lines indicate EC50 values. An increase in EC50 values is observed with increasing NO donor concentrations.

Fig. 3A depicts the dependence of the half maximum constant EC50 as a function of the NO donor concentration in a log − log plot. EC50 values are averaged over n ≥ 3 experiments. A liner fit of the dependence of log(EC50)vs. log (PAPA/NO) reveals a slope of 0.5± 0.2 which is not statistically different from 1/2(p = 0.946). The above data point towards an EC50 value proportional to the square root of the NO donor (PAPA/NO) i.e. EC50[NOdonor]. Thus, experiments point towards an EC50 value that is linearly dependent on the square root of NO donor and as a result proportional to the clamped NO concentration, i.e. EC50 ∝ [NO].

FIGURE 3.

FIGURE 3

(A) A log – log graph of half maximum constant (EC50) at different PAPA/NO concentrations. Average EC50 values (n = 3) are presented. The slope of 0.5 ± 0.2 is not statistically different from 0.5 (p = 0.946). The result suggests that EC50 is proportional to the square root of NO donor concentration and thus proportional to NO concentration. (B) A graph of EC50 vs. clamped NO values from NO electrode measurements in Fig 1B. The slope from a linear fit of the graph is 30.5 ± 5.2 μM GSH/μM.

NO donor concentrations were related to NO concentrations using experimental data from Fig. 1B. (Alternatively, one can use Eq. 1d if the stoichiometry and half – life of the NO donor is known). We then can plot EC50 values from Fig. 3A as a function of [NO] (Fig. 3B). A linear dependence is observed in Fig. 3B with a slope of 30.5 ± 5.2 μM GSH/μM NO.

EC50=30.5[NO] Eq. (4)

Experiments were repeated in a chemiluminescence analyzer following the 2C assay method from Gaston et al. [73] using different DEA/NO and GSH concentrations. This NO donor had a reasonably short half –life so as to allow both for a “clamped NO” condition (over a short period of time), and provide an early elimination of NO donor from the solution. The latter condition is needed to avoid interferences in the chemiluminescence device due to NO release by the donor when GSNO levels are measured. Recordings were collected for each GSH and NO donor concentration and were compared against a predetermined calibration curve prepared from known concentrations of GSNO(data not shown). Rates of GSNO formation were obtained by dividing GSNO concentrations by the corresponding incubation/reaction times. The control experiments where GSNO content was abolished with HgCl2 showed zero signal, hence confirming that the signal obtained was from GSNO. The estimated GSNO production rates were used to calculate EC50 using curve fitting similar to Fig. 2B. A slope of 0.38 ± 0.07 in the log EC50 vs log [DEA/NO] data was estimated (n = 3). This is slightly different than the slope of approximately 0.5 from the earlier method. This may be attributed to some GSNO scavenging during the hour-long post reaction incubation time (see methods section). However, the alternative explanation for participation of N2O3 in nitrosation of GSH cannot be excluded.

Calculation of k5

This constant applies to the overall reaction of NO2· with both the thiol and the thiolate anion and it is pH dependent[31] (See also table T1). Based on our analysis the dependence of EC50 on [NO] is linear with a slope that is equal to k4k2(k-2+k4)k5. Then assuming the values for the other kinetic constants (k2, k−2, k4) from Table 1 and a slope of 30.5 μM GSH/μM NO from Eq. 3 a value for k5 of 1.15 × 107 M−1s−1 is predicted. This is essentially the same as the experimentally observed value by Ford et al. [31], (derived from Fig. 2 in [31] for pH = 7.4), and reasonably close to their corrected estimate of 2 × 107 M−1s−1 which takes account the reduction of GS at higher pH values in their analysis. The rate constant of N2O3 hydrolysis (Reaction 4) was determined from Eq. 9 and accounts for catalysis by 40mM of phosphate [18,44], i.e. K4 = (530 + KP [Pi]) where kp = 9.4×105 M−1s−1[18,44].

Table T1.

Rate constants of reactions mentioned in the manuscript are as follows:

Reaction No. Reaction Rate constant Reference
1
2NO+O2k12NO2
k1 = 2.9×106 M−2s−1 [44, 58]
2
NO+NO2k-2k2N2O3
k2 = 1.1×109 M−1s−1
k−2 = 8.1×104 s−1
[18]
[18]
3
N2O3+GSHk3GSNO+NO2-+H+
k3= 6.6×107 M−1s−1 [33]
4
N2O3+H2Ok42NO2-+2H+
k4= 3.8×104 s−1 [18]
5
N·O2+GSHk5NO2-+GS·+H+

N·O2+GS-k5NO2-+GS·
k5= 1.15×107 M−1s−1
(k5=k5+k5[GS-][GSH])
Estimated
See also [31]
6
GS·+N·Ok6GSNO
k6= 3×109 M−1s−1 [66]
7
GSHk-7k7GS-+H+
k7= 63 s−1
k−7= 0.1×1010 M−1s−1
[46]
[46]*
8
GS·+GS-k-8k8GSSG-
k8= 9.6×106 M−1s−1
k−8 = 1.6×105 s−1
[26]
[47]
9
GSSG-+O2k9GSSG+O2·-
k9= 5×109 M−1s−1 [47]
10
GS·+GSNOk10GSSG+N·O
k10= 1.7×109M−1s−1 [50]
*

pH = 7.4

Dependence of Vmax on [NO]

In Fig. 4A, we plot Vmax against PAPA/NO concentrations in a log − log plot. A slope of 1.09 ± 0.1 in the log − log plot suggests a linear dependence between Vmax and [PAPA/NO] (i.e. a square dependence on [NO] in agreement with both kinetic mechanisms). A linear plot of Vmax vs [PAPA/NO] reveals a slope of (7.5 ± 0.5) ×10−5 s−1(Fig. 4B).

FIGURE 4.

FIGURE 4

(A) A log – log graph of nitrosation rates at saturating GSH concentrations (Vmax) at different PAPA/NO concentrations. Average values with standard deviations (error bars) are presented. A linear fit gives a slope of 1.08 ± 0.1. The slope is not statistically different from 1 (p = 0.09) and significantly different from 0.5 and 1.5 (p ≪ 0.05) suggesting a Vmax proportional to the NO donor concentration. (B) The linear dependence of Vmax on PAPA/NO concentration has a slope of (7.5 ± 0.5) × 10−5 s−1.

Vmax=7.5×10-5[PAPA/NO] Eq. (5a)

Based on both kinetic mechanisms (Eq. 2a or 2b) Vmax = 2k1[NO]2[O2]. [Note: Eqs 2c & d predict different Vmax dependence on NO and differences with Eq. 2b can become significant at high GSH or GSNO concentrations. However, experimental data and model simulations (see below) suggest that under our experimental conditions these differences are negligible].

Using Eq. 1d, and the previously determined value for n×kd=1.58 ± 0.03 × 10−4s−1 from the electrode data, we predict that:

Vmax=2k1[NO]2[O2]=nkd2[NOdonor]=7.9×10-5[PAPA/NO] Eq. (5b)

Thus, the observed dependence of Vmax on PAPA/NO is in agreement with theoretical analysis for both kinetic mechanisms.

Validation of rate law and data fitting

To validate the assumptions in the pseudo steady state approximation, we compared the proposed rate law (Eq. 2b) with the numerical solution of the complete set of ordinary differential equations describing the second kinetic mechanism (Reactions 1, 2, 4, 5, and 6) and assuming values for kinetic constants from Table 1. Rate law and numerical solution provide essentially identical results (data not shown). Thus, Eq. 2b accurately describes the behavior of the second kinetic mechanism.

We further validated the proposed rate laws (Eq. 2b2d) against our experimental data and we tested if measured GSNO formation rates are in agreement with predicted rates from the rate laws. Previously determined values for reaction rate constants were assumed (Table 1). Each NO donor concentration was related to the corresponding clamped NO concentration based on Eq. 3. In Fig. 5 rate law predictions are presented as solid lines and experimental data with different symbols for each NO donor (or NO) concentration. Dotted lines depict model simulations of the set of all 25 reactions presented in the Supplement. From the three rate laws, only Eq. 2d is shown. Eq. 2b and 2c yield similar results as 2d over the range of GSH examined, and hence they were omitted from Fig. 5. There is close agreement between rate law, model simulations and experimental data over a wide range of NO and GSH concentrations. There is a difference between rate law and model for high NO indicating that additional reactions that have not been incorporated in the simplified kinetic mechanism become more important as NO concentration increases. The accuracy of the experimental data does not allow confirming this limitation of the rate law at high NO concentrations.

FIGURE 5.

FIGURE 5

Comparison of GSNO formation rates as predicted by the proposed rate law of the simplified reaction scheme Eq. 2d (solid lines), the mathematical model of the complete reaction set (dotted lines) next to experimental data. Data using different PAPA/NO concentrations are presented (500 μM, 1 mM, 3 mM, 5 mM and 10 mM). The corresponding NO concentration achieved were. Error bars show standard deviations (n = 3).

Eq. 2c suggests that when the ratio of [NO] to [GSH] is not much greater than k8k7k6k7 reactions 79 become important. Based on previous estimates for constants k6, k7, k−7, and k8 (Table 1) this ratio should be equal to 5×10−4μM NO/μM GSH. In the experimental results presented in Fig. 5, the ratios of [NO]/[GSH] were between 10−3–10−1 thus, these reactions should not have affected GSNO formation. In the supplement, we present model simulations for higher GSH concentrations (Fig. S1). GSNO formations rates show a decrease at high [GSH] that cannot be captured by the rate law of Eq. 2b. On the contrary, Eq. 2c is in agreement with model simulations suggesting that this effect is attributed to Reactions 79.

Eq. 2d suggests that when [GSNO]k6k10[NO] Reaction 10 does not affect formation rate. By measuring formation rates within a few seconds after mixing of the reactants we can minimize the effect of this reaction. At longer times, when [GSNO] approaches k6k10[NO], an effect of this reaction can be observed(data not shown). Thus, under our experimental conditions and for the range of NO and GSH concentrations examined Reactions 1, 2, 4, 5, and 6 are the ones that mostly determine GSNO formation rate.

Discussion

Recent evidence for contribution of NO2 radical in the nitrosation of thiols [8, 16, 22, 39] provided the incentive to revisit an earlier proposed kinetic law by Kharitonov et al. [17] for the nitrosation of thiols. We followed a similar theoretical analysis (i.e. PSSA) with this earlier study for two alternative reaction schemes; one where N2O3 is the nitrosating intermediate and one where NO2 plays this role. Earlier experimental data have confirmed saturation kinetics of the nitrosation rate on GSH concentration [7, 17, 36]. This is in agreement with both kinetic mechanisms. Previous studies however, did not examine if the GSH concentration for half-maximum rate (i.e. EC50) remains constant at different NO concentration levels. Theoretical analysis suggests that unlike in N2O3-based nitrosation, in a primarily NO2-based nitrosation the EC50 will increase as the NO concentration increases.

Experimental findings in this study confirm such dependence and argue for significant contribution of the second kinetic mechanism in GSH nitrosation. Our data show that GSNO formation rate follows saturation kinetics with respect to GSH concentration and EC50 increases with NO donor concentration. Data suggests an EC50 that is proportional to [NO] (Fig. 3). This is in agreement with NO2 based nitrosation (Eq. 2b).

Theoretical considerations corroborated by experimental data show that in aerated slow-releasing NO donor solutions, NO levels remain relatively steady with a concentration that increases proportionally to the square root of the NO donor concentration (Fig. 1). This enables us to monitor the reaction over longer periods of time (i.e. no need for rapid mixing in a stop-flow apparatus) and to relate the rate of GSNO formation to the NO concentration. [Caution however is advised since at later times conversion of GSNO to GSSG might influence GSNO formation rate]. We utilized two alternative methods to assess GSNO concentration. With the spectrophotometrical method, GSNO is measured continuously during the reaction, while chemiluminescence requires stopping the reaction at different time points and assess GSNO after a long incubation time to release excess NO from the system. As a result, rates estimated with the second method may have less accuracy.

Goldstein et al [18] has previously suggested that NO2 can act as an active intermediate for GSH nitrosation. They presented kinetic laws that propose a functional difference between NO2 and N2O3 mechanisms similar to this study (Note: Eq. 21 and 22 in [18] propose similar saturation kinetics but for the nitrosation yield instead of the reaction rate). These two quantities should follow a similar dependence on GSH and NO, at initial times. This functional difference was tested for some thiols (NAPenSH) showing dependence characteristic of the N2O3 based pathway. The authors concluded that both NO2 and N2O3 can play the role of active intermediate in thiol nitrosation.

Schrammel et al [8] have provided evidence for NO2 as the main nitrosating intermediate for GSH and albumin. The nitrosation was partially inhibited in the presence of thiyl scavengers (ascorbate and TEMPOL) and EPR spectroscopy revealed intermediate formation of glutathionyl radicals. They concluded that GSNO formation by NO/O2 is predominantly mediated by NO2. However, TEMPOL may not impact solely the thiyl radical since scavenging of NO2 has also been suggested [41]. This would presumably interfere with the N2O3 pathway as well (Reaction 3). Jourd’heuil et al. [39] have also provided evidence for NO2 over N2O3 as the nitrosating intermediate. Inhibition of thiyl radical-mediated GSNO and GSSG formation by the thiyl radical trap 5,5-dimethyl-1-pyrroline N-oxide (DMPO) was demonstrated. However, nitrosation was shown to be insensitive to DMPO in an earlier study [40]. Thus, although the recent use of spin traps has provided evidence for a significant role of NO2 in thiol nitrosation, the relative importance of the two alternative intermediates remains a topic of continuing investigations. A recent study by Keszler et al [22] utilizes theoretical analysis and experimentation and suggests involvement of both intermediates in nitrosation. Simplified rate laws were provided for N2O3 but not for NO2 nitrosation. A detailed kinetic model that includes 20 relevant reactions was proposed and was fitted to the experimental data. Evidence for N2O3 contribution is provided by the reported decrease in GSNO formation when N2O3 hydrolysis is enhanced. A 10-fold increase in the rate of N2O3 mediated nitrosation (Reaction 3) than previously reported was actually suggested to explain a decrease in GSSG with a concomitant increase in GSNO when a thiyl radical trap (DMPO) was utilized. This allows for significant increase in GSNO formation through mechanism 1(N2O3 based nitrosation scheme) when mechanism 2 (NO2 based nitrosation scheme) is inhibited. Thus, there is conflicting evidence for the effect of thiyl radical scavenging on GSNO formation with some studies reporting a decrease [8, 39] while others an increase [22, 65]. However, as pointed outin [22], cross talk between the two pathways makes difficult the interpretation of the results and to conclusively determine which is the dominant mechanism.

There is a good agreement between our estimated kinetic constant for thiol oxidation by NO2 (i.e. k5 = 1.15×107 M−1s−1) and the constant provided by Ford et al. [31] (i.e 1×107 M−1s−1 and 2 ×107 M−1s−1 after correction for a side reaction). Based on this value the authors in this earlier study argued, that there is small likelihood for significant generation of N2O3 (Reaction 2) compared to the loss of NO2 via reaction such as Reaction 5, and thus, a substantial fraction of any NO2 produced should not be channeled to nitrosative chemistry involving N2O3. This suggests a dominant role of NO2 in nitrosation of thiols and a lesser role for N2O3. Our theoretical analysis demonstrates this point in a system containing a significant number of the most relevant reactions.

An important observation in previous studies [22, 39, 40, 65] is the significant generation of GSSG. Reactants and active intermediates may be utilized for the generation of GSSG and this utilization can affect GSNO formation rate. This represents a serious threat for the accuracy of the proposed simplified rate laws (Eq. 2a and Eq. 2b) presented here or in previous studies. The reaction scheme presented in the supplement proposes four alternative pathways for GSSG formation (Reactions 8, 10, 11, 18) out of which Reactions 8 and 10 are the most important based on the assumed values for the kinetic constants. Interestingly, Reaction 8 becomes important for low [NO]/[GSH] ratios while Reaction 10 is important after significant GSNO accumulations and thus high [GSNO]/[NO] ratios. Thus, the proposed rate law in Eq. 2b can adequately describe our data since the high [NO]/[GSH] ratio and the estimation of GSNO formation rate early (i.e. low [GSNO]/[NO] ratio) should provide conditions for low GSSG formation rate. [Note that previous studies [22, 39, 40, 65] have often used lower [NO]/[GSH] ratios and reaction is followed for several minutes]. Interference from Reaction 8 will occur at low [NO]/[GSH] ratios and will be documented with a decrease in GSNO formation rate as GSH concentration increases (Fig. S1). Interference from Reaction 10 will appear after significant GSNO accumulation and will be documented with a saturation of GSNO concentration with time. In this study, the nitrosation mechanism was tested only for glutathione. Previous studies have shown similar kinetic behavior in the nitrosation of Cysteine, whereas for other thiols like N-acetyl Penicillamine (NAPenSH), captopril (CapSH) and N-nitrosomorpholine (MorNNO) the oxidizing reaction through NO2 has been found to be too slow and Reaction 2 was found to outcompete their oxidation by NO2 [18].

In vivo, the nitrosation pathway could be affected by the slow NO oxidation and other reaction pathways could become important. It has been previously suggested [16, 19, 20, 21, 25, 28], that catalysis of nitric oxide oxidation in hydrophobic environments is possible which might accelerate formation rate. The physiological relevance of the nitrosation process and the ability of thiols to transport and preserve NO might hinge on acceleration of nitrosation in hydrophobic environments (owing to < 1 μM [NO] in vivo and the slow NO oxidation process in aqueous solution), and thus this needs further study. In addition, the effects of transition metal ions [27], cellular antioxidants [29] and lipid radical species [30]and pH variations [31] need to be further examined. There is also a possibility of a heme enzyme dependent nitrosation[67]. Glutathione may bind to ferric cytochrome c followed by a combination of NO to form a ferric cyt-c GSNOH complex. Subsequent electron donation from NO to heme would then, yield ferrous cytochrome c and GSNO. Experimental evidence with isolated enzymes and in cells corroborate this hypothesis [68]. Besides cytochrome c, other heme enzymes and iron complexes may serve similar functions [69, 70, 71, 72].

In summary, recent studies point towards a role of NO2 in thiol nitrosation. However, the relative contribution of N2O3 and NO2 has been difficult to elucidate so far, as a result of cross talk between the two alternative mechanisms. In this study, theoretical analysis suggests a functional difference in the rate laws between N2O3 and NO2 mediated nitrosation (Eq. 2a and 2b) and experimental data suggest a predominant role for NO2 in the nitrosation of GSH by NO donors in aerated solutions. In vivo, a series of factors may interfere with the nitrosation pathway and the relative importance of the two intermediates needs to be further investigated.

Supplementary Material

01
02

Acknowledgments

This work was funded by National Institutes of Health Grant SC1HL095101 (NT).

Footnotes

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