pitfalls of peroxynitrite determination by luminescent probe in diabetic rat aorta
TRANSCRIPT
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Pitfalls of peroxynitrite determination by luminescentprobe in diabetic rat aorta
Andras Nemeth • Krisztian Stadler • Judit Jakus •
Tamas Vidoczy
Received: 15 November 2011 / Accepted: 20 January 2012 / Published online: 9 February 2012
� Akademiai Kiado, Budapest, Hungary 2012
Abstract Pitfalls of peroxynitrite (ONOO-) formation in diabetic rat aorta on
luminol-induced chemiluminescence (LCL) are investigated based on a detailed
reaction mechanism in a case where 1.0 9 10-7 M s-1 superoxide formation rate
and nitric oxide (•NO) formation were measured by electron paramagnetic reso-
nance, while ONOO- formation by LCL. Modeling ONOO- formation at equi-
molar reactant ratio at pH 7.4 and 37 �C predicts 2.0 nM ONOO- and
2.1 9 10-6 M steady-state •NO concentrations, which are both biologically rele-
vant. Comparison of steady-state concentrations to those obtained by modeling the
LCL intensity at pH 10 shows that ONOO- concentration increases with 10% while
peroxynitrous acid (ONOOH) concentration decreases complying with the pH shift.
Evaluation of steady-state reaction rates reveals that the contribution of CO3•-
radicals to the formation of luminol radicals is 76%, that of •NO2 is 24%, consid-
erable, but that of •OH radicals negligible. The contribution of additional superoxide
formation by autoxidation of luminol is 13%, not negligible, but that of ONOOH
homolysis is negligible. The •NO2 is predominantly formed from the decomposition
of the ONOO-–carbon dioxide adduct and only 0.5% directly from •NO oxidized
by molecular oxygen. But the contribution of the latter pathway depends strongly on
the •NO and superoxide formation rate ratio, at a ratio of 2:1, it would increase to
A. Nemeth (&) � K. Stadler � J. Jakus
Institute of Biomolecular Chemistry, Chemical Research Center, Hungarian Academy of Sciences,
Pusztaszeri ut 59-67, Budapest 1025, Hungary
e-mail: [email protected]
Present Address:K. Stadler
Oxidative Stress and Disease Laboratory, Pennington Biomedical Research Center, Baton Rouge,
LA 70808, USA
T. Vidoczy
Institute of Structural Chemistry, Chemical Research Center, Hungarian Academy of Sciences,
Pusztaszeri ut 59-67, Budapest 1025, Hungary
123
Reac Kinet Mech Cat (2012) 106:1–10
DOI 10.1007/s11144-012-0427-3
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14%. The measured time interval of the initial increase of LCL intensity complies
with the time needed luminol aorta outside and inside concentrations in the sample
to be equalized by diffusion, the 7 9 10-3 s-1 rate constant obtained by modeling
enabled to estimate 5 9 10-7 cm2 s-1 as the diffusion coefficient of luminol in the
diabetic rat aorta.
Keywords Peroxynitrite � Luminol � Chemiluminescence � Reaction mechanism �Modeling
Introduction
Luminol (LH,5-amino-2,3-dihydro-1,4-phthalazinedione) induced chemilumines-
cence (LCL) is one of the most frequently applied methodologies for peroxynitrite
(ONOO-) detection [1, 2]. It has a high selectivity with a detection limit
1 9 10-9 M min-1 for ONOO- fluxes by photon counting [2] and 1 9 10-11 M
for ONOO- concentration by applying a membrane sampler [3]. Luminol is
endosomal membrane permeable [4] and its initial oxidation step, converting
luminol to luminol radical cannot be achieved by superoxide (O2•-) [5].
The LCL probe in biological systems, however, cannot directly asses the
formation of a particular reactive intermediate, since different reactive species can
lead to the formation of the light-emitting species. An early study by Faulkner et al.
[6] argued that in the presence of molecular oxygen, the univalently oxidized
luminol itself can be a source of superoxide formation. Recently, a comprehensive
review advanced by Wardman [7] on the pitfalls of the luminol probe for reactive
oxygen and nitrogen species called attention to the impact of nitric dioxide and
concluded that quantification of mechanistic pathways would be required for the
rational use of the probe.
In accordance with this recommendation, the goal of the present study was to
address (i) the effect of pH shift, a technique used to intensify LCL intensity, (ii) the
implications of additional superoxide formation, (iii) the competition between nitric
dioxide (•NO2), carbonate radical anion (CO3•-) and hydroxyl radical (•OH) in the
production of luminol radicals, (iv) the contribution of peroxynitrous acid
(ONOOH) homolysis, and (v) that of nitric oxide (•NO) oxidation to the formation
of •NO2 by modeling based on a detailed reaction mechanism.
Experimental
Most of the experimental data are from our already reported work [8]. Three-week-
old male Wistar rats were kept under standard conditions then randomly divided
into diabetic and age-matched control groups containing 6–8 animals for each
experiment. To induce diabetes, animals were anesthetized and STZ was injected
via the vena femoralis. Induction of diabetes was confirmed by measuring the
urinary glucose level 3 days later. 1, 2, 3, and 7 weeks after the onset of diabetes,
control and diabetic rats were exsanguinated under anesthesia.
2 A. Nemeth et al.
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To determine the rate (spin clearance) of in vivo formation of oxygen-centered
free radicals in the aorta, rats received the spin probe 3-carbamoyl-proxyl
(c-PROXYL), 56 mg kg-1 i.p. at 5, 10 and 15 minutes before sacrificing. Then,
organ samples were prepared in liquid nitrogen and electron paramagnetic
resonance (EPR) signal intensities were registered. Co-administration of the
superoxide dismutase (SOD) enzyme with c-PROXYL revealed that the majority of
the formed oxygen-centered free radicals was superoxide. The accumulation and
decay of c-PROXYL were measured between 5 and 30 min and registered EPR
signal intensities from six diabetic aorta pieces were evaluated by double integration
using an EPR analysis program. Intensities in arbitrary units were calibrated with
2,2,6,6-tetramethylpiperidine-N-oxyl (TEMPO), a stable free radical.
Electron paramagnetic resonance measurements and spin trapping procedures
were carried out with an X-Band computer-controlled spectrometer constructed by
Magnettech GmbH (Berlin, Germany). Approximately 100 mg of tissue samples
were frozen into a rod-shaped form and spectra of the samples were recorded at
77 K using a quartz finger-Dewar filled up with liquid nitrogen. Instrument settings
were 100 kHz modulation frequency, 0.7050 mT modulation amplitude, 18 mW
microwave power, 1 min scan time and 20.63 mT field sweep. For the evaluation of
the EPR signals, Mn/MnO as an internal standard was used.
A luminol-dependent chemiluminescence method originally described by Zweier
et al. [9] and modified by Brovkovych et al. [10] was used to measure ex vivo
ONOO--derived radical generation in the rat aorta tissue (each sample weighing
8–10 mg) placed in 2 mL Hanks buffer solution (pH 7.4), and starting photon
counting immediately after luminol addition. In another series of measurements,
1 mL alkaline sodium bicarbonate-luminol solution was added to the sample (final
concentrations were 400 mM of luminol, 50 mM of bicarbonate.
Method of modeling and reaction mechanism
First, the fate of ONOO- was modeled by a CO2-only consumption of ONOO-
yielding the biologically maximum ONOO- concentration at pH 7 and 37 �C [11].
The NO formation rate, taking into account that in biological systems ONOO-
related effects are generally observed at equimolar reactant rates of ONOO-
formation was set to be equal to that measured for superoxide. Then, modeled
steady-state concentrations were compared to those obtained by modeling LCL
intensity at pH 10 when luminol and bicarbonate solutions were added to the sample
and reactions of luminol appended to the mechanism. Finally, contribution analysis
of the steady-state reaction rates was carried out to assess the impact of pitfalls on
LCL intensity.
The reaction mechanism compiled from the literature is shown in Table 1. Their
rate constants are at pH 7.4 and 37 �C, when not indicated otherwise. If data were
not available under these conditions, we used the closest obtainable value. Reactions
(1–17) consist of the reduced set of ONOO- formation and decomposition based on
the consideration that in a biological environment the reactions of ONOO- with
CO2 outcompetes other decay process [14]. In order to account for the impact of
Pitfalls of peroxynitrite determination by luminescent probe 3
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Table 1 Reaction mechanism
No. Reaction k or pK Reference
1 •NO ? O2•- ? ONOO- 1.6 9 1010 M-1 s-1 [25]
2 ONOO- ? CO2 ? ONOOCO2- 3.0 9 104 M-1 s-1 [26]
3 ONOOCO2- ? •NO2 ? CO3
•- 6.5 9 108 s-1 [27]
4 ONOOCO2- ? NO3
- ? CO2 1.25 9 109 s-1 [27]
5 2O2•- (?2H?) ? O2 ? H2O2 2.0 9 105 M-1 s-1 [28]
6 O2•- ? CO3
•- ? O2 ? CO32- 6.5 9 108 M-1 s-1 [29]
7 •NO ? CO3•- ? NO2
- ? CO2 3.5 9 109 M-1 s-1 [29]
8 2•NO ? O2 ? 2•NO2 2.9 9 106 M-2 s-1 [30]
9 •NO ? •NO2 ? N2O3 1.1 9 109 M-1 s-1 [29]
10 N2O3 ? •NO ? •NO2 8.4 9 104 s-1 [29]
11 N2O3 (?H2O) ? 2NO2- ? 2H? 5.22 9 104 s-1 [30, 32]
12 •NO2 ? O2•- ? O2NOO- 4.5 9 109 M-1 s-1 [33]
13 O2NOO- ? •NO2 ? O2•- 1.1 s-1 [33]
14 O2NOO- ? NO2- ? O2 1.3 s-1 [33]
15 2•NO2 ? N2O4 4.5 9 108 M-1 s-1 [29]
16 N2O4 ? 2•NO2 6.9 9 103 s-1 [29]
17 N2O4 (?H2O) ? NO2- ? NO3
- ? 2H? 1.0 9 103 s-1 [31]
18 ONOOH ? •NO2 ? •OH 0.35 s-1 [35]
19 •NO2 ? •OH ? ONOOH 4.5 9 109 M-1 s-1 [35]
20 •OH ? •OH ? H2O2 5.5 9 109 M-1 s-1 [34, 36]
21 •NO2 ? •OH ? NO3- ? H? 4.5 9 109 M-1 s-1 [34]
22 O2•- ? SOD ? SODred
- ? O2 2.0 9 109 M-1 s-1 [40]
23 O2•- ? SODred (?2H?)?H2O2 ? SOD- 2.0 9 109 M-1 s-1 [40]
24 Tyrosine ? CO3•- ? tyr-O• ? HCO3
- 4.5 9 107 M-1 s-1 [29]
25 Tyrosine?•NO2 ? tyr-O• ? NO2- ? H? 3.2 9 105 M-1 s-1 [41]
26 Tyr-O• ? •NO2 ? 3-nitrotyrosine 1.3 9 109 M-1 s-1 [31, 41, 42]
27 Tyr-O• ? O2•- ? P1 1.5 9 109 M-1 s-1 [43]
28 Tyr-O• ? •NO ? Tyr-ONO 1.0 9 109 M-1 s-1 [31, 44]
29 Tyr-ONO ? Tyr-O• ? •NO 1.0 9 103 s-1 [31, 44]
30 Tyr-ONO ? P2 1.8 9 10-1 s-1 [31]
31 2Tyr-O• ? 3,3-dityrosine 2.25 9 108 M-1 s-1 [44]
32 ONOOH $ ONOO- ? H? 6.6 [46]
33 CO2 ? H2O $ H? ? HCO3- 6.1 [37, 38]
34 HCO3- $ H?? CO3
2- 10.3 [37, 38]
35 LHins- ? CO3
•- ? LH• ? CO32- 9.0 9 108 M-1 s-1 [7]
36 LHins- ? •NO2 ? LH• ? NO2
- 1.0 9 106 M-1 s-1 [7]
37 LHins- ? •OH ? LH• ? -OH 9.0 9 109 M-1 s-1 [7]
38 LH• ? O2•- ? light ? APht (pH 10) 2.0 9 105 M-1 s-1 [46]
39 LH• ? O2 ? Lox ? O2•- 6.0 9 102 M-1 s-1 [39]
40 LHouts ? LHins 7 9 10-3 s-1 This work
The symbol tyr-O• indicates the tyrosyl radical, P1 substituted indole-2-carboxylic acids [23], P2 3-ni-trotyrosine or hydrolysis products [47]. APht is ground state aminophthalate [12], Lox is 5-aminophthal-azine-1,4-dione [47], subscripts outs and ins denote luminol sample outside and inside, respectively
4 A. Nemeth et al.
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•OH radicals on the production of luminol radicals, its production by homolysis of
ONOOH and corresponding termination reactions were added, reactions (18–21).
The impact of the biological environment on ONOO- formation and decay is much
more complex and its reaction mechanism is less elaborated [12, 13]. A mechanism
was recently suggested to model tyrosine nitration by superoxide and •NO fluxes in
biological systems as well as a mechanism for the role of SOD [14]. These reactions
(22–31) were assumed for the present case as well. SOD is a powerful superoxide
scavenger found practically uniformly distributed within the cell, operating as a
drain of excess O2•-. Species derived from tyrosine are not quantitatively important
since they represent a tiny fraction of ONOO- consumed, but their importance lies
in their stability and the use as the trail of ONOO- in vivo. Efficient ONOO-
scavengers, such as peroxiredoxin, some thiol proteins, glutathione peroxidase, and
several heme proteins could not be taken into account because their concentrations
were not known in the investigated system. Reactions (32–34) set the constraints for
the equilibrium between ONOO- and ONOOH, and the carbonates.
The oxidation potential of luminol was also thoroughly investigated, reactions
(35–39). The initial step of oxidation is the interaction between LH- and radicals
CO3•-, •OH, and •NO2 producing LH• radicals. Here we note that the rate constant
of the latter interaction is known only from personal communications of Merenyi as
already referred to in [7], estimated to be at least 106 M-1 s-1. Next, addition of
O2•- produces a rather unstable endoperoxide, which decomposes very fast into
excited aminophthalate and nitrogen, the former leading subsequently to the
emission of chemiluminescence. Luminol radicals can react with oxygen to generate
O2•-, where Lox is 5-aminophthalazine-1,4-dione.
The effect of luminol diffusion, reaction (40) will be discussed in the next
chapter. KINAL software was used to model the reaction mechanism and fit to
measured data to extract the contribution from the reactions of interest [15].
Results and discussion
A fixed parameter of the kinetic analysis was the experimentally determined
1.0 9 10-7 M s-1 superoxide formation rate. The initial concentration for oxygen
was taken as 1.0 9 10-5 M, for total carbon dioxide (CO2 ? HCO3-) as
1.4 9 10-3 M, for tyrosine as 1.0 9 10-3 M, these being the usual values in
plasma as already referred to in [14], 5.5 9 10-6 M for SOD the average of its
biological relevant range in the present case as earlier modeled by us [16],
4 9 10-4 M for luminol and 50 mM for bicarbonate.
Complying with the experiments ONOO- formation and decay was first modeled
at pH 7.4 and 37 �C, conditions at which the superoxide formation rate was
measured. For the reason discussed above, the rate of •NO formation was set to
1.0 9 10-7 M s-1 the measured rate of superoxide formation. The predicted
2.0 9 10-9 M ONOO- and 2.1 9 10-6 M •NO steady-state concentrations are in
biologically relevant ranges as already referred to in [11]. Steady-state concentra-
tions and reaction rates obtained were compared to those obtained by modeling LCL
at pH 10 when luminol and bicarbonate solutions were added to the sample.
Pitfalls of peroxynitrite determination by luminescent probe 5
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In this modeling, however, we were confronted with the problem that the
measured LCL intensity showed an expressed time dependence approaching a
maximum after a time lag of approximately 20 min (vide measured curve in Fig. 1).
This observation was seemingly in contradiction with the steady-state condition
prevailing in the sample. We assumed that the discrepancy could be the
consequence of the experimental procedure, and hypothesized that this time
dependence was related to the time required for the luminol concentration to reach
its equilibrium within the sample (since CO2 diffuses much faster, there was no need
to take its diffusion into consideration by a similar approach). Therefore, the
reaction mechanism was amended by reaction (40) where indices outs and ins
denote luminol concentrations aorta outside and inside in the sample. Since the
measured LCL intensity was available only in arbitrary units (cps) the computed
rate of luminol radical formation which is directly related to the rate of light
producing reaction was normed to the maximum cps value measured. By the trial
and error method, an acceptable fit between the time dependence of measured and
computed curves was obtained at k40 = 7 9 10-3 s-1 (Fig. 1). The descending part
of the measured curve following the maximum was possibly due to deteriorating
cell functioning in our in vitro system. The hypothesis was also confirmed by
plotting inner and outer luminol concentrations against time (Fig. 2), illustrating
that they became equal within the recorded time lag.
In Table 2, modeled changes of steady-state concentrations are summarized. The
concentrations of both O2•- and •NO are significantly affected, but their product, i.e.,
the rate of ONOO- formation in less measure. The increase of ONOO-
concentration was 10%, the ONOOH concentration decreased complying with the
pH shift while their sum remained unchanged. Modeling indicated a shift from
NO2- to NO3
- accumulation. The consumption of tyrosine was negligible.
0 500 1000 1500 2000 2500 3000
time, s
0
1000
2000
3000
4000
5000
6000
7000
8000
9000
LCL
inte
nsity
, cps
(LH
. xO2.-
xk37
) no
rmed
to c
ps
calculated
measured
k39= 7.0x10-3 s-1
Fig. 1 Evaluation of luminol diffusion rate constant in rat aorta: fitting the time dependence of the rate ofLH• formation (normed to cps) to that of measured LCL (in cps)
6 A. Nemeth et al.
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In order to asses the effect of pitfalls on LCL intensity, which is directly related
to the rate of LH• radical formation, contribution analysis was carried out. This
revealed that the contribution of luminol autooxidation to O2•- formation was 13%,
not negligible but that of ONOOH homolysis negligible. The contribution of CO3•-
radicals to LH• radical formation was 76%, that of •NO2 24%, a considerable impact
on LCL intensity, while that of •OH radicals negligible.
With regard to the pivotal role of •NO2, the contribution of pathways to its
formation were also evaluated. In the present case, •NO2 was predominantly formed
via the decomposition of the ONOOCO2- adduct and only 0.5% directly from • NO
0 400 800 1200time, s
0E-01
1E-04
2E-04
3E-04
4E-04
5E-04
conc
entr
atio
n, M
LH-ins
LH-outs
Fig. 2 Evaluation of the time interval of initial increase in LCL intensity: modeled luminolconcentrations outside and inside of a rat aorta sample in function of time
Table 2 Impact of luminol
and pH shift on steady-state
concentrations
pH 7.4 pH 10
M M Change, %
LH- 4.0 9 10-4
O2•- 2.4 9 10-12 4.2 9 10-12 75
•NO 2.1 9 10-6 1.3 9 10-6 -38
ONOO- 2.0 9 10-9 2.2 9 10-9 10
ONOOH 4.9 9 10-10 1.4 9 10-12 -100
ONOO- ? ONOOH 2.5 9 10-9 2.5 9 10-9 &0•NO2 2.3 9 10-11 2.4 9 10-11 4
CO3•- 5.2 9 10-13 8.0 9 10-14 -85
•OH 1.2 9 10-10 1.4 9 10-19 &-100
NO3- 5.6 9 10-5 6.4 9 10-5 14
NO2- 4.1 9 10-5 2.7 9 10-5 -34
Tyrosine 1.0 9 10-3 1.0 9 10-3 &0
3-Nitrotyrosine 2.2 9 10-7 1.4 9 10-7 -36
Tyr-ONO 1.6 9 10-8 6.5 9 10-9 -59
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oxidized by molecular oxygen. It follows, however, from the reaction mechanism,
that the contribution of the latter pathway is strongly related to the •NO–superoxide
formation rate ratio. A computational exercise showed that 15% of •NO2 would be
formed through this bypass way at 2:1 •NO–superoxide formation rate ratio. The
reaction graph of corresponding reaction pathways and contributions are illustrated
in Fig. 3.
As an additional result, from the diffusion rate constant k40, an approximate value
5 9 10-7 cm2 s-1 as bulk diffusion coefficient of luminol in the diabetic rat aorta
was calculated by a method already referred to in [14]. The diffusion coefficient of
luminol in 0.1 M NaOH solution is 6.6 9 10-6 cm2 s-1 [17, 18]. In biological
systems, such data are not known to us, but values were reported for •NO in
liposomes and for red blood cells to be half [19–21], and in rat aorta wall to be
nearly fourfold less than in water [22]. The calculated value is less than that
suggested by this analogy. The difference might be attributed to the harmful effect
of diabetes. The literature supports this explanation as diabetes mellitus [23] and
related hypertension [24] lead to increased rat aorta rigidity.
Conclusions
Modeling rendered useful information on possible pitfalls of ONOO- determination
by LCL. It confirmed that neither the impact of •NO2 nor the contribution of the
autoxidation of luminol producing additional superoxide formation can be
neglected. On the other hand, frequently discussed pitfalls, such as the impact of
ONOO−
ONOOCO2−
ONOOH
O2
O2•−
CO2
•NO
85%
15%
•NO2
~0%
NO2-
NO3-
Fig. 3 Contribution of reactionpathways to the formation andconsumption of •NO2 radicalsmodeled at nitric oxide–superoxide formation rate ratio2:1 and pH 10, in percentage
8 A. Nemeth et al.
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ONOOH hydrolysis on •NO2 formation and the impact of •OH radical on LCL
intensity, seem to be minor in the present case. It also demonstrated that the pH shift
affected the steady-state concentrations. It is, however, recognized that doubts can
arise regarding the oversimplifications we were forced to apply, but which at the
same time emphasize an authentic need for new and better data obtained in
biological systems.
Acknowledgment Helpful discussion with Professor I Papai on the carbonate equilibrium was
gratefully acknowledged.
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