Document gbZL4a9o7wzoyxewQ7n57z8wN
Proc. Nati. Acad. Sci. USA Vol. 81, pp. 1696-1700, March 1984 Biochemistry
Mutagenicity of quinones: Pathways of metabolic activation and detoxification
(benzola]pyrene quinones/oxygen radicals/NADPH-cytochrome P-450 reductase)
PAUL L. CHESIS*, DAVID E. LEVIN*, MARTYN T. SMITHt, LARS ERNSTERt, AND BRUCE N. AMES*
Departments of *Biochemistry and tBiomedical and Environmental Health Sciences, School of Public Health, University of California, Berkeley, CA 94720;
and tDepartment of Biochemistry, Arrhenius Laboratory, University of Stockholm, S-10691 Stockholm, Sweden
Contributed by Bruce N. Ames, December 12, 1983
ABSTRACT The mutagenicity of various quinones, a class of compounds widely distributed in nature, is demonstrated in the Salmonella TA104 tester strain. The metabolic pathways
by which four quinones, menadione, benzo[alpyrene 3,6-qui-
none, 9,10-phenanthrenequinone, and danthron, caused mutagenicity in this test system were investigated in detail as were the detoxification pathways. The two-electron reduction of these quinones by NAD(P)H-quinone oxidoreductase (DT-diaphorase) was not mutagenic, whereas the one-electron reduction, catalyzed by NADPH-cytochrome P-450 reductase, was mutagenic, except for danthron, which was only slightly mutagenic. The mutagenicity of the quinones via this pathway was found to be attributable to the generation of oxygen radicals. The cytochrome P-450 monooxygenase also played a significant role in the detoxification and bioactivation of these quinones. For example, phenanthrenequinone was converted to a nonmutagenic metabolite in a cytochrome P-450-dependent reaction, whereas danthron was converted to a highly mutagenic metabolite. These studies show the complexity of metabolic pathways involved in the mutagenicity of quinones.
Quinones are widely distributed in nature, and human exposure to them is extensive. The quinones of polycyclic aromatic hydrocarbons are abundant in all burnt organic material, including automobile exhaust, cigarette smoke, and urban air particulates (1-3). Quinones are also found naturally in many of the foods we eat (4-6), and compounds containing the quinone nucleus are widely employed as antitumor agents (7, 8). Despite the magnitude of this human exposure, the pathways by which many quinones are metabolized remain poorly understood and their mutagenicity is largely untested. In a recent study, however, six naturally occurring naphthoquinones, including menadione, were shown to be mutagenic to strain TA2637 with metabolic activation (9), indicating the need for further studies.
Quinones serve as substrates for a wide variety of flavoenzymes, including NADPH-cytochrome P-450 reductase, NAD(P)H-quinone oxidoreductase (DT-diaphorase), NADHcytochrome b5 reductase, and NADH-ubiquinone oxidoreductase, and can undergo either a direct two-electron reduction to the hydroquinone or a one-electron reduction to the semiquinone radical (10-13). In the presence of oxygen most semiquinones rapidly autooxidize to form the superoxide anion radical (02.) and thus regenerate the quinone (14). This redox cycling can lead to conditions of oxidative stress through the production of 02 (15) and has been invoked to explain the cytotoxic and antitumor properties of quinonoid drugs (16). We have recently demonstrated that the xanthine oxidase-dependent superoxide-generating system is mutagenic to the new Salmonella tester strain TA104 (unpublished). This finding suggested that the redox cycling of qui-
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nones might also be mutagenic, and we have tested this possibility using the TA104 strain, which is sensitive to a wide variety of oxidative mutagens (17). We have also attempted to characterize the pathways by which several different quinones are metabolized and to study the potential mutagenicity of the metabolites and side products formed. We therefore decided to investigate only those quinones that required metabolic activation to exhibit mutagenicity. To limit the scope of this project we also chose not to study quinones that possess reactive leaving groups. Quinones of this type have been shown to interact with DNA via a methide reaction (18-20).
MATERIALS AND METHODS
Materials. Glucose 6-phosphate (Glc-6-P), NADP+, deoxycholate, sodium dilauroyl diphosphotidylcholine, dicoumarol, bovine serum albumin, superoxide dismutase (SOD), and thymol-free catalase were obtained from Sigma; NADPH and NADH were from Calbiochem-Behring; and Glc-6-P dehydrogenase was from Boehringer-Mannheim (Mannheim, F.R.G.). SKF525A (proadiphen, 2-diethylaminoethyl-2,2diphenyl valerate) was a gift of Smith Kline & French.
Danthron (1,8-dihydroxyanthraquinone) was from Aldrich. Menadione (2-methyl-1,4-naphthoquinone) was from Sigma. The benzo[a]pyrene quinones were a gift of the National Cancer Institute. The diesel exhaust quinones, 9,10phenanthrenequinone and a mixture of 1,6- and 1,8-pyrene quinones (1), were the gift of Dennis Scheutzle of Ford Motor Company.
Enzyme Preparations. S9 liver homogenate was prepared from polychlorobiphenyl-induced rats as described (21). For the mutagenicity tests with S9 the standard enzyme preparation (50 ,ul of S9 diluted to 0.5 ml per plate) was used (21). For some of these assays (Table 1) NADH was substituted for NADP+/Glc-6-P in the S9 enzyme preparation. In these tests NADH was added at twice the molar level of NADP+ and Glc-6-P because the oxidation of each Glc-6-P molecule normally produces two NADPH.
Purified NADPH-cytochrome P-450 reductase (22) was the generous gift of Bettie Sue Masters. Incubations with P450 reductase contained 50 ,g of sodium dilauroyl diphos-
phatidylcholine, 25 ,ug of deoxycholate, 2 /imol of NADPH,
2 ,umol of Glc-6-P, 1 unit of Glc-6-P dehydrogenase, and 2.5 ,ug of purified P-450 reductase diluted to 0.3 ml with 0.2 M KPO4 (pH 7.6). The P-450 reductase was added last to prevent its precipitation from solution. This preparation was made just prior to use and kept on ice.
Mutagenicity Assays. All mutagenicity assays were performed with the Salmonella tester strain TA104 using a liquid preincubation procedure (21). The quinones were dissolved in dimethyl sulfoxide and added to sterile 13 x 100 mm capped culture tubes, followed by addition of 0.2 M NaPO4
Abbreviations: DT-diaphorase, NAD(P)H-quinone oxidoreductase; SOD, superoxide dismutase; Glc-6-P, glucose 6-phosphate.
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Biochemistry: Chesis et al.
Proc. Natl. Acad. Sci. USA 81 (1984) 1697
Table 1. Effect of dicoumarol, NADPH, and NADH on S9-mediated quinone mutagenicity
His+ revertants per plate
Quinone
Concentration, AM
NADPH
NADPH and dicoumarol
NADH
Menadione
60 124 20 211 26 15 6
Benzo[a]pyrene 1,6-quinone 30 577 113 582 104 317 55
Benzo[a]pyrene 3,6-quinone 30 890 140 866 127 315 47
Benzo[a]pyrene 6,12-quinone
90
182 14 201 18 120 9
Pyrene 1,6- + 1,8-quinones
60 1171 212 1204 195 458 53
9,10-Phenanthrenequinone
60
50 6
48 9
18 4
Danthron
60
748 94
740 101 395 33
Quinone concentrations were chosen near the high end of the linear dose-response region. All assays contained S9 and were performed by using the preincubation method (see text). The NADPH S9 preparation contained NADP+ at 4 mM and Glc-6-P at 4 mM. The production of NADPH is dependent on endogenous soluble enzymes present in the S9. The NADH S9 preparation contained NADH
at 8 mM. Dicoumarol was used at 30 AM. Data points represent the mean SD of the number of
induced revertants in at least three experiments.
(pH 7.4) (S9 assays) or 0.2 M KPO4 (pH 7.6) (P-450 reductase assays), with or without SOD, catalase, SKF525A, or dicoumarol and 0.1 ml of an overnight culture of the bacterial strain. The enzyme preparation was added last, bringing the total volume to 0.5 ml for the P-450 reductase assays and 1.0 ml for the S9 assays. All preincubation mixtures were brought to 0.1% bovine serum albumin to help stabilize soluble enzymes and to prevent the addition of SOD or catalase (or both) from altering the total protein concentration. The tubes were incubated with shaking for 30 min at 30C. Two milliliters of molten top agar containing histidine and biotin were then added, the mixture was plated on minimal glucose, and the plates were scored after 48 hr.
Biochemical Assays. The contribution of DT-diaphorase to the NADPH-dependent reduction of the different quinones by rat liver S9 was determined as the dicoumarol-inhibitable rate of quinone-stimulated NADPH oxidation (10). The change in absorbance was followed at 340 nm, and an extinction coefficient of 6.22 mM-1 cm-' was used. Each reaction mixture contained 10 ,ul of S9, 2.5 mM NADPH, 0.08% Tri-
ton X-100, and N30AM quinone brought to a final volume of 1
ml with 50 mM Tris-HCl (pH 7.5). Dicoumarol was used at 30 ,M and addition of NADPH was used to start the reaction.
Superoxide anion (02*) production was measured as the reduction of succinylated cytochrome c with the wavelength
pair of 550-557 nm and an extinction coefficient of 21 mM-1 cm'1 (23, 24). Each reaction mixture contained 50 ,g of dilauroyl phosphatidylcholine, 25 ,ug of deoxycholate, 1 jimol of NADPH, 2 jimol of Glc-6-P, 1 unit of Glc-6-P dehydro-
genase, 0.5 mg of succinylated cytochrome c, 0.25 ,ug of NADPH-cytochrome P-450 reductase, and 30 ,uM quinone in dimethyl sulfoxide brought to a final volume of 1.0 ml with 0.2 M KPO4 (pH 7.6). All reactions were initiated by addition of the quinone. The specificity of the reaction for 02 was tested by the addition of 30 units of SOD.
RESULTS
Effect of Dicoumarol on S9-Mediated Quinone Mutagenicity: Role of the Two-Electron Reduction Pathway. The mutagenicity of different quinones representing a variety of chemical classes was tested in the presence and absence of dicoumarol (30 ,uM) by using liver S9 as the bioactivation system and the Salmonella tester strain TA104. Dicoumarol is a potent inhibitor of DT-diaphorase (10), which catalyzes the direct two-electron reduction of quinones to hydroquinones (11, 13, 15). By selectively inhibiting DT-diaphorase, it was thus possible to assess the contribution of this pathway to the mutagenic activity of the different quinones. The data shown in Table 1 reveal that the addition of dicoumarol had no significant effect on the mutagenicity of any of the
quinones except menadione. Menadione was approximately twice as mutagenic when dicoumarol was present. Dicoumarol alone showed no significant mutagenicity in this sys-
tem.
All of the quinones tested that showed mutagenicity in this
system were more mutagenic in the presence of NADPH than NADH, indicating a prominent role for NADPH-cytochrome P-450 reductase in mediating quinone mutagenicity (Table 1). Of the quinones tested, 1,6- and 1,8-pyrene quinones were the most mutagenic. Both benzo[a]pyrene 1,6quinone and benzo[a]pyrene 3,6-quinone were also highly mutagenic but benzo[a]pyrene 6,12-quinone was a relatively weak mutagen in this system, as were menadione and phen-
anthrenequinone (Table 1). Danthron was also mutagenic (Table 1), in agreement with previous findings with other tes-
ter strains (25).
Four of the quinones-namely, menadione, danthron, phenanthrenequinone, and benzo[a]pyrene 3,6-quinone were selected for further study. Menadione is a naphthoquinone that is readily reduced via NADPH-cytochrome P450 reductase to its semiquinone radical (15). Danthron is an anthracene quinone of much greater stability but structurally related to the anthraquinone antibiotics, such as Adriamycin, which are used in cancer chemotherapy (16, 25). Phenanthrenequinone is present in diesel exhaust and urban air particles (1, 3) and benzo[a]pyrene 3,6-quinone is prevalent in much combusted material, including automobile exhaust (1, 2). The relative ability of these four quinones to serve as substrates for the two-electron pathway catalyzed by DTdiaphorase was determined by measuring their respective rates of dicoumarol-inhibitable NADPH oxidation in the liver S9 preparation (Table 2). Menadione is known to be an
Table 2. Relative rates of DT-diaphorase-catalyzed reduction of quinones with S9 measured as dicoumarol-inhibitable NADPH oxidation
NADPH oxidation, nmol/min
Quinone
Dicoumarol-
Concen-
inhibitable rate
tration,
S9 and (DT-diaphorase
,uM S9 dicoumarol activity)
Menadione
30 76.3
Benzo[a]pyrene
3,6-quinone
30 9.9
9,10-Phenan-
threne-
quinone
30 41.9
Danthron
30 5.8
6.4 5.9
9.7 3.2
69.9 4.0
32.2 2.6
Values represent the mean of duplicate experiments.
1698 Bio'chemistry: Chesis et aL
excellent substrate for DT-diaphorase (10, 13, 15), but, interestingly, phenanthrenequinone also appeared to serve as a good substrate for this enzyme (Table 2). On the other hand, both benzo[a]pyrene 3,6-quinone (26) and danthron were relatively poor substrates.
Ability of NADPH-Cytochrome P-450 Reductase to Catalyze the Mutagenicity of the Different Quinones. To further test the role of NADPH-cytochrome P-450 reductase in catalyzing the mutagenic activity of the above quinones and to elucidate the role, if any, of other enzymes in the S9 preparation involved in their metabolism, we replaced the S9 preparation with purified P-450 reductase in the test system. The results in Fig. 1 show that phenanthrenequinone, menadione, and benzo[a]pyrene 3,6-quinone were all highly mutagenic when the purified reductase was used as the bioactivation system, whereas danthron was only slightly mutagenic. These results are virtually the reverse of those seen when the liver S9 preparation was used (compare Table 1 and Fig. 1).
To test the possible role of oxygen radicals in the reductase-mediated mutagenicity of the above quinones to TA104, we measured the mutagenicity of each quinone in the presence of SOD and catalase. All four quinones showed similar patterns, with SOD inhibiting mutagenesis partly, catalase inhibiting to a greater extent than SOD, and the two together inhibiting the reductase-mediated mutagenicity almost completely (Fig. 1). Based on these findings we predicted that there should be a close correlation between the relative rates
Of 02T production and the mutagenicity of these quinones with NADPH-cytochrome P-450 reductase. By measuring the SOD-inhibitable reduction of succinylated cytochrome c, we were able to quantitate relative rates of 02 formation
Menadione 1000 _
Benzo(a)pyrene3,6-quinone
800-
6C608000
P450 Reductase
400~~~~~~~~~~~
&.SOD200
RedPu4c5t0ase
400
FIG. 1.
60
&+sooAT~
Ait of
pA
41)0-0Q0uinon4e50 e ~ ~ ~ i+ O
cyohrm -45-Phenanthsean dte Danethro O n aaae l
ossaycson000 ned2.5uun h UPe-S4c5O0DAT~~~a~~~~~~~~~p ~CA
SOD
~I ~AT
0 24 6
0 24 6
Quinone (PuM)
FIG. 1. Relative mutagenicity of quinones with purified NADPH-
cytochrome P-450 reductase and the effect of SOD and catalase. All
assays contained 2.5 u.g of the P-450 reductase and were performed
by using the preincubation method (see text). SOD and catalase were used at 25 units each per plate. The mutagenicity of the different quinones is shown with P-450 reductase alone (o) and also in the presence of SOD (A), catalase (CAT) (U), or SOD and catalase together (e).
Proc. NatL Acad. Sci. USA 81 (1984)
for the four different quinones (Table 3). In direct agreement with their relative mutagenicities, phenanthrenequinone was the most potent 02 generator, being almost twice as potent as menadione, which in turn was far more potent than danthron. Interestingly, the benzo[a]pyrene 3,6-quinone-stimulated reduction of succinylated cytochrome c catalyzed by the reductase was quite appreciable, being slightly more than half that observed with menadione, which could be in agreement with their relative mutagenicity. However, in contrast to menadione, SOD addition had little or no effect on the rate of cytochrome c reduction.
Role of the Cytochrome P-450 Monooxygenase in the Detoxification and Bioactivation of the Different Quinones. The S9 and P-450 reductase enzyme preparations gave very different patterns of mutagenesis for the above quinones. Having ruled out the two-electron reduction pathway as the cause of this variation, we realized that there must be another pathway(s) leading to mutagenic activation of some quinonesnotably, danthron-and the detoxification of others. To investigate the possibility that this NADPH-dependent pathway involved the cytochrome P-450 monooxygenase system, we studied the effect of adding the cytochrome P-450 inhibitor SKF525A (proadiphen) (27) to the S9 preparation. The effect of adding SOD and catalase to the S9 preparation was also examined. The results (Fig. 2) demonstrate that each of these four quinones is metabolized quite differently by enzymes present in the S9 preparation.
The mutagenicity of menadione was not significantly affected by the addition of SKF525A, but it was largely inhibit-
ed by SOD and catalase (Fig. 2). Both SKF525A and SOD/
catalase inhibited the mutagenic activity of benzo[a]pyrene 3,6-quinone to some extent (Fig. 2). The mutagenicity of phenanthrenequinone was greatly increased by the addition of SKF525A (Fig. 2). This increase in mutagenicity could be inhibited by SOD and catalase (Fig. 2). Finally, we found that the mutagenicity of danthron was largely inhibitable by SKF525A, but it was not significantly affected by SOD and catalase (Fig. 2).
DISCUSSION
A systematic analysis of the metabolism of four quinones namely, menadione, phenanthrenequinone, danthron, and benzo[a]pyrene 3,6-quinone-to mutagenic metabolites by rat liver S9 preparation and purified hepatic NADPH-cytochrome P-450 reductase has been performed by using the new Salmonella TA104 tester strain. Each of the quinones studied required metabolic activation to become mutagenic. None of the quinones tested showed decreased mutagenicity when DT-diaphorase was selectively inhibited with dicoumarol, thus indicating that the two-electron reduction pathway does not contribute to the mutagenic activation of these four quinones. This is in contrast to quinones possessing reactive leaving groups that have been shown to be converted
Table 3. Relative rates of NADPH-cytochrome P-450 reductasecatalyzed production of 02 with quinones measured by reduction of succinylated cytochrome c
Succinylated cytochrome c reduced, ,umol/min per mg of
protein
Quinone
No With SOD-inhibitable
addition SOD
rate
Menadione
35.8 1.0
Benzo[a]pyrene 3,6-quinone 19.1 16.0
9,10-Phenanthrenequinone 91.4 5.5
Danthron
3.4 1.5
34.8 3.1 85.9 1.9
Values represent the mean of duplicate experiments. All quinones were added to a final concentration of 30 ,uM.
Biochemistry: Chesis et aL
Benzo(a)pyrene3, 6-quinone
S9
* +SKF
/*(I)
SKF OD
c: co
6) a0:)
~C003
20 40 60
0 20
Quinone (j4M)
FIG. 2. Effect ofSKF525A and SOD/catalase on the mutagenic-
ity of quinones with S9. Quinone concentrations were chosen that
gave linear dose-response curves. All assays contained S9 and dicoumarol (30 AM) and were performed by using the preincubation
method (see text). SOD and catalase were used at 25 units each per
plate. SKF525A was used at 0.2 mM. The mutagenicity of the different quinones is shown with S9 alone (o) and also in the presence of
(A).SKF525A (SKF) (A), SOD plus catalase (CAT) alone (e), or in com-
bination
to mutagens by DT-diaphorase (18-20). In the case of the naphthoquinone menadione, the mutagenicity was increased by the inhibition of DT-diaphorase. This finding supports the contention that this enzyme serves a protective role against menadione cytotoxicity (13, 15) and is consistent with the observation that menadione is an exceptionally good substrate for DT-diaphorase (10). Thus, DT-diaphorase is essentially a detoxification pathway for some quinones (Fig. 3, pathway B).
Using purified NADPH-cytochrome P-450 reductase, it
was shown that these four quinones are activated to muta-
gens by a one-electron reduction pathway (Fig. 3, pathway
ACTIVATION
DETOXI FICATION
Cytochrome P-450
Cytochrome P-450
FIG. 3. Schematic illustration of pathways involved in quinone mutagenesis.
Proc. Natl. Acad. Sci USA 81 (1984) 1699
A). In all cases this mutagenesis was inhibited by SOD and catalase. This finding indicates that the one-electron reduction of these quinones to semiquinones is mutagenic via the formation of O2 and, subsequently, H202. The conclusion that it is the oxygen radicals rather than the quinones themselves or their semiquinone metabolites that are mutagenic is further supported by the correlation found between superoxide production and mutagenicity.
One possible complication is the case of benzo[a]pyrene 3,6-quinone. Table 3 shows that the P-450 reductase-dependent reduction of this quinone leads to the reduction of cytochrome c in the absence of significant 2 formation. It is plausible that the species reducing cytochrome c in this case is benzo[a]pyrene 3,6-diol. This could explain the failure of SOD to inhibit the reduction of cytochrome c in the presence of benzo[a]pyrene 3,6-quinone. However, SOD and, to a greater extent, catalase inhibit the mutagenicity of this quinone in TA104 (Fig. 2), suggesting that its mutagenicity is mediated via oxygen radicals. The oxygen radicals could
arise from the autooxidation of benzo[a]pyrene 3,6-diol rather than from the semiquinone intermediate reacting with oxygen. This, under the assay conditions employed for 027 formation, the benzo[a]pyrene 3,6-diol could reduce the cytochrome c and be oxidized back to the quinone without generating 02, whereas under the mutagenicity assay conditions benzo[a]pyrene 3,6-diol could accumulate and autooxi-
dize, generating 02 and H202 in the process (28). The cytochrome P-450 monooxygenase system also seems
to play a significant role in either the detoxification or muta-
genic activation of these quinones (Fig. 3, pathway C). The relative contribution of this pathway and the P-450 reductase-dependent pathway (Fig. 3, pathway A) to the observed mutagenicity of the different quinones was therefore evaluated. This was done by adding SKF525A, a potent inhibitor of cytochrome P-450 (27), and/or SOD/catalase to the S9 enzyme preparation. Because the mutagenicity of menadione was inhibited by SOD/catalase, we conclude that it is attributable to the O2 and H202 formed by redox cyclingi.e., pathway A is the prevalent activation mechanism (Fig. 3). With benzo[a]pyrene 3,6-quinone, both SKF525A and SOD/catalase inhibit mutagenesis to some extent, and because these inhibitors act in an additive fashion it seems likely that both pathways A and C (Fig. 3) contribute to the mutagenicity of this quinone. The fact that the benzo[a]pyrene quinones are mutagenic in this new tester strain raises again the question of the role of the metabolites in benzo[a]pyrene carcinogenesis (29).
Phenanthrenequinone exhibited an altogether different pattern of mutagenesis. When the S9 enzyme preparation was used alone, there was a very low level of mutagenicity that was inhibitable by SOD and catalase. The addition of SKF525A greatly increased this mutagenicity, but this increase was still inhibitable by SOD and catalase. These re,sults indicate that this quinone is usually converted to a nonmutagenic (nonredox cycling) metabolite by the cytochrome P-450 monooxygenase system (Fig. 3, pathway D). Inhibition of this enzyme system allows the quinone to enter pathway A (Fig. 3) and act as a substrate for the P-450 reductase, thus leading to the production of oxygen radicals and mutagenesis in TA104. The final quinone tested was danthron. This quinone was found to be a very poor redox cycler but a good substrate for the cytochrome P-450 monooxygenase system. However, unlike phenanthrenequinone, the metabolite of danthron formed by this enzyme system was highly mutagenic in TA104-i.e., pathway C is the prevalent activation mechanism (Fig. 3).
In conceiving this project it was hoped that generalizations might be found concerning the metabolic activation of quinones to mutagens. Instead it was found that the observed level of mutagenesis was dependent on a series of pathways,
1700 Biochemistry: Chesis et aL
each of which acts differently on the four quinones analyzed. Fig. 3 summarizes these findings but does not take into account the fact that the detoxification of quinones may occur via a glutathione S-transferase pathway (30, 31). However, conjugation with reduced glutathione does not prevent Zertain quinones from redox cycling and generating oxygen radicals (32). The role of glutathione in protecting against quinone mutagenicity therefore requires further study. This work demonstrates that the correlation between mutagenic characteristics and the structure of quinones is complex, depending on both their chemical properties and their ability to interact with cellular enzymes. Quinones are very abundant in nature and continue to show promise as antitumor agents, indicating that their mutagenicity and carcinogenicity are areas worthy of future investigation.
We are grateful to Dennis Schuetzle for the diesel exhaust quinones and to Larry Marnett for helpful discussions. We are also particularly indebted to Bettie Sue Masters for a very generous supply of pure NADPH-cytochrome P-450 reductase. B.N.A. was supported by DOE Contract DE-AT03-76EV70156 and by the National Institute of Environmental Health Sciences Center Grant ES01896, and M.T.S. was supported by the National Foundation for Cancer Research.
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