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Plant Physiol, November 2000, Vol. 124, pp. 1293-1304 Analysis of Oxidative Stress and Wound-Inducible Dinor Isoprostanes F1 (Phytoprostanes F1) in Plants1Julius-von-Sachs-Institute, Pharmaceutical Biology, University of Wuerzburg, Julius-von-Sachs-Platz 2, D-97082 Wuerzburg, Germany
Isoprostanes F2 are arachidonate autoxidation products
in mammals that have been shown to be induced during several human disorders associated with enhanced free-radical generation.
Isoprostanes F2 represent not only extremely reliable
markers of oxidative stress in vivo, but they also exert potent
biological effects. Therefore, it has been postulated that
isoprostanoids are mediators of oxidant injury in vivo. Higher plants,
however, do not synthesize arachidonic acid or isoprostanes. Here we
show that a series of isoprostane F2 analogs termed
phytoprostanes F1 (previously dinor isoprostanes
F1) are formed by an analogous pathway from
Free radical-catalyzed oxidation of
arachidonate has been shown to lead to a complex isomeric mixture of
prostaglandin-like compounds termed isoprostanes. Isoprostanes have
attracted considerable attention since it has been shown that
isoprostanes are formed in mammals at concentrations that exceed the
levels of enzymatically formed prostaglandins by at least an order of
magnitude (Morrow and Roberts, 1997 Higher plants generally do not synthesize the precursor arachidonate
required for isoprostane formation, but rather utilize
We have recently elucidated the phytoprostane pathway in plants and
have established that a group of prostaglandin/isoprostane E1- and F1-like compounds
is formed in plant cells in vivo (Parchmann and Mueller, 1998 Prostanoid analysis in plant tissues is further complicated by the
occurrence of acyclic trihydroxylated fatty acid derivatives (Fig.
2) that have the same
Mr as the cyclic trihydroxylated fatty acid
isomers of the PPF1-type. Acyclic triols show
similar chromatographic mobilities as prostanoids and may erroneously
be identified as prostaglandins in various prostaglandin immuno- and
bioassays (Hamberg and Gardner, 1992
Preparation of PPE1 and PPF1 PPE1 and PPF1 were
produced by autoxidation of
Purification, Identification, and Quantification of PPF1 Autoxidation of linolenic acid as described above yields a complex
mixture of peroxidized compounds. Endoperoxy and hydroperoxy groups of
the reaction products were reduced to the corresponding hydroxy
compounds by incubation of the autoxidation mixture with triphenylphosphine (1 g/g linolenic acid) for 30 min. A purification method was developed using tritiated prostaglandin
F2 The mixture of PPF1, theoretically comprised of
32 isomers, was analyzed by HPLC. PPF1 were
partially resolved on a C18 reversed phase HPLC column (Fig.
3). GC-electron impact (EI)-MS analysis of the HPLC peaks after methylation and silylation of the samples showed that only peaks denoted with 1 to 4 eluted as single peaks from
the GC column. PPF1 regioisomers were identified
by their EI spectra (Fig. 4, A and B).
PPF1 type I and type II reference spectra were
recorded from PPF1s obtained by
NaBH4 reduction of authentic
PPE1 type I and type II compounds (Parchmann and
Mueller, 1998
High resolution MS revealed that PPF1 regioisomers
produce ions (Fig. 4, A and B) at m/z 217.1074 (C9H21Si2O2,
trimethylsilyl [TMS]-O-CH=CH-CH=O+-TMS) and
191.0928 (C7H19Si2O2,
TMS-O+=CH-O-TMS). These ions are
indicative for F-ring prostanoids as they are generated by
intramolecular rearrangement reactions of the cyclopentane F-ring
system (Roberts et al., 1998 The methyl ester TMS ether derivatives of PPF1 type I and II were also analyzed by positive chemical ionization-MS (Fig. 4, C and D). The predominant ions produced from type I and II compounds are the molecular ion [M+H]+ at m/z 559 and three fragments at m/z 469, 379, and 289 derived from the sequential cleavage of TMS-OH from the three TMS ether groups of the molecules. The intensity of these ions varies greatly among different PPF1 isomers. It is not possible to differentiate type I and II compounds by their chemical ionization spectrum. PPF1 were also analyzed as their corresponding
pentafluorobenzyl (PFB)-ester, TMS derivatives by GC-MS in the negative
ion chemical ionization (NICI) mode, which is an extremely sensitive detection method for prostanoids. NICI spectra of
PPF1 type I and II were identical, displaying
only one major fragment ion at m/z 543 corresponding to the
[M-PFB] Synthesis of Oxygen-18-Labeled PPF1 GC-MS analysis requires an appropriate internal standard. In the case of PPF1, which represents a mixture of 32 isomers, the use of a commercially available C20 homolog such as PGF1 would be straightforward, but unlikely to be reliable since various PPF1 isomers and PGF1 probably would have different chromatographic properties and ionization efficiencies. The most appropriate retention time and quantification standard was found to be an isotopically labeled PPF1 isomer mixture, which was prepared by oxidation of linolenate in an oxygen-18 atmosphere. GC-MS analysis of oxygen-18 labeled PPF1 revealed that each isomer contained three [18O]hydroxy groups as predicted by the mechanism of formation (Fig. 1) and that the GC peak pattern matched exactly that of the unlabeled PPF1 isomer mixture (data not shown). An unlabeled PPF1 standard solution of known concentration (see "Materials and Methods") was used to quantify the mixture of [18O]3PPF1 by GC-NICI-MS. GC-NICI-MS of Phytoprostanes in Plant Material The most sensitive method for quantifying prostanoids by GC-MS
described in the literature involves analyzing the PFB ester, TMS ether
derivatives in the NICI mode. A drawback of the method is, however,
that various enzymatically and nonenzymatically formed acyclic,
trihydroxylated derivatives of linolenate cannot be differentiated from
PPF1s since they may behave similar on GC-MS and
would yield ions of identical mass (O'Connor et al., 1984
Assay Parameters and Validation The recovery of PPF1 in different steps of the sample preparation method was estimated by spiking 300 mg of lime tree flowers (dry powder) with [5,6,8,9,11,12,14,15-3H]PGF2 (specific activity of 179.00 Ci/mmol) prior to work-up. Recovery of radioactivity after various processing steps was determined by scintillation counting. Ether extraction (used for the measurement of free PPF1) and modified Folch extraction/base hydrolysis (used for the determination of esterified plus free PPF1), as well as the following silica solid phase extraction step were all performed with a recovery greater than 90%. After full sample preparation 60.57% ± 1.48% and 31.27% ± 8.97% of the radioactivity were recovered in samples containing free and total PPF1, respectively. The quantification of endogenous PPF1 was performed by using [18O]3PPF1 as an internal standard by comparison of the intensity of the peaks at m/z 545 co-eluting with the peaks of the internal standard at m/z 551. The lower limit of detection of PPF1 (signal to noise ratio of 5:1) is in the range of 100 pg. Several procedures were performed to establish the accuracy of this assay. Precision was measured by analyzing aliquots of tobacco cells (170 mg of dry weight) obtained from a cell suspension culture 3 d after transfer to fresh medium. The mean of six replicate measurements of the ratio of m/z 545 to m/z 551 was found to be 1.07% ± 0.16% and corresponded to a concentration of 36.67 ± 5.77 ng/g of dry weight. Accuracy was assessed using aliquots of the same tissue. For this, 10 to 1,500 ng of unlabeled PPF1 and 500 ng of [18O]3PPF1 were added to eight sample aliquots that were re-assayed in triplicate. A linear relationship between added and found PPF1 was documented (r = 0.9890). The amount of endogenous PPF1 measured in the precision experiment was subtracted from the total measured and the accuracy of the assay to measure the added 10 to 1,500 ng of PPF1 was calculated. The accuracy of PPF1 determinations varied with the level of PPF1 to be measured (Fig. 6).
PPE1 and PPF1 Are Formed in Plant Cells in Vivo Levels of PPE1 and PPF1 in free and esterified form in peppermint leaves, chosen as a representative example, were determined. In fresh peppermint leaves, the concentrations of unesterified phytoprostanes were 76 ± 4 ng/g of dry weight of PPF1 and 37 ± 5 ng/g of dry weight of PPE1. Levels of esterified PPF1 and PPE1 (11,240 ± 1,520 and 130 ± 4 ng/g of dry weight, respectively) were one to two orders of magnitude higher than those of free phytoprostanes (Table I). PPF1 Levels Are Wound Inducible To clarify if the large PPF1 accumulation observed in harvested peppermint leaves (Fig. 5) is an early event triggered by wounding of living plants or occurs by autoxidation of lipids in dead plants we wounded fresh peppermint leaves with a nail stamp (12 nails/cm2). Time-dependent PPF1 accumulation was measured over 6 h after wounding (Fig. 7, E and F). The concentration of free PPF1s increased and reached a maximum level of 192 ng/g of dry weight (more than 4-fold over control levels) within 1 h and declined thereafter. A second increase was observed after 3 h. Levels of esterified PPF1 rose after wounding, reached a maximum level of 4,000 ng/g of dry weight (more than 5-fold over control levels) after 1.5 h and decreased thereafter. The PPF1 isomer distribution was found to be similar to that of the synthetic [18O]3PPF1 standard. Thus wounding appears to be accompanied by formation of free radicals, which trigger an appreciable synthesis of free and esterified PPF1.
Although accumulation of PPF1 in wounded plants does take place, levels of PPF1 are well below the levels found in dried, stored plant powders, suggesting that massive PPF1 formation takes place in dead plant material during storage. Exogenous Addition of Butyl Hydroperoxide or Cupric Acetate Results in Dramatic Accumulation of PPF1 in Plant Cells To assess the effect of oxidative stress on PPF1 levels in plant cells, California poppy (Eschscholzia californica) cell suspension cultures were treated with 10 mM t-butyl hydroperoxide. A dramatic increase of esterified PPF1 followed by an increase of free PPF1 was observed. Levels of esterified PPF1 started to increase within 30 min and reached maximal levels (12 µg/g of dry weight) after 4 to 5 h (Fig. 7B). Levels of free PPF1 increased after 3 h and reached a transient maximum (1.6 µg/g of dry weight) after 12 h (Fig. 7A). In additional experiments, California poppy suspension cells were treated with 500 µM cupric acetate. A biphasic induction of PPF1 levels was observed. Levels of esterified PPF1 began to increase after a lag phase of 2 to 3 h and reached a first maximum (20 µg/g of dry weight) 6 h after copper(II) ion administration. Thereafter, PPF1 levels declined and rose again after 14 h (Fig. 7D). Levels of free PPF1 began to increase after a lag phase of about 4 h, reached a first maximum (2.8 µg/g of dry weight) after 9 h, declined thereafter, and increased again after 15 h (Fig. 7C).
Occurrence of Prostaglandin-Like Compounds in Plants Since the discovery of prostaglandins in mammals, several reports
have appeared describing the identification of prostanoids in plants
and microorganisms (for review, see Bundy, 1985 Analysis and Occurrence of PPF1 For GC-NICI-MS analysis of PPF1, an optimized sample preparation protocol has been established that largely removes acyclic trihydroxylated fatty acids. In addition, PPF1 could be differentiated from remaining acyclic triols by MS after catalytic hydrogenation. Nonenzymatically formed PPF1 yield a characteristic peak pattern in GC-NICI-MS chromatograms. The PPF1 signature has been found in autoxidized linolenate samples, autoxidized plant drugs, in untreated cell cultures and plants, in copper(II) ion and peroxide stressed plant cell cultures, as well as in wounded plants. We also demonstrated that PPF1 occur in free and
esterified form in plants. Esterified PPF1 are
likely located in membrane lipids as has been shown for isoprostanes
F2 in mammals (Morrow et al., 1992 In the species so far analyzed, levels of esterified PPF1 were one to two orders of magnitude higher than free PPF1. Furthermore, in butyl hydroperoxide or copper(II) ion treated cells, as well as in wounded plants, levels of esterified PPF1 increased earlier and reached higher levels than free PPF1 (Fig. 7), suggesting that reactive oxygen species (ROS) initiate PPF1 synthesis in membrane lipids. However, if lipase-dependent release of PPF1s from membranes occurs in plants remains to be shown. In an alternate manner, it may be assumed that linolenate is liberated
from membrane stores in various pathophysiological situations and may
serve as precursor for free PPF1. In the case of
tissue injury by wounding, it has previously been shown that injury of
tomato plants is accompanied by generation of ROS (Orozco-Cardenas and
Ryan, 1999 It is apparent that plants accumulate higher levels of
PPF1 than PPE1. The
preferential formation of PPF1 is compatible with the concept that biosynthesis of phytoprostanes occurs in a hydrophobic environment such as a membrane, which would stabilize the endoperoxide intermediate and favor PPF1, rather than
PPE1 formation (Fig. 1; Table I). In addition,
nonenzymatic reduction of free and membrane-bound endoperoxide
intermediates to F-ring prostanoids by glutathione appears to be more
rapid than rearrangement of the endoperoxide intermediates to E-ring
prostanoids, at least in mammals (Morrow et al., 1998 Isoprostanoids as Marker of Oxidative Stress in Vivo Perhaps the best established aspect of isoprostanoid research is
the finding that isoprostanes can be used as a quantitative index of
lipid peroxidation in humans. As they are chemically stable end
products of lipid peroxidation they appear to be more reliable and
accurate markers of oxidative stress than other oxidation products such
as malondialdehyde, especially in vivo (Roberts and Morrow, 1997 Here we show that PPF1s accumulate in oxidatively
stressed plant cells. Our preliminary findings suggest that
PPF1s may be useful as indicators of oxidative
stress in plants. For instance, hydroperoxides and copper ions that are
known to initiate lipid peroxidation (Frankel, 1998 Isoprostanoids May Deteriorate Membrane Integrity Leading to Cell Death Formation of ROS, lipid peroxidation, loss of membrane integrity,
and cell death are typical features of many abiotic stresses and the
hypersensitive reaction of plants against incompatible microorganisms.
ROS are thought to function as a signal that may induce defense gene
activation and programmed cell death. In addition, excessive formation
of ROS leads to cellular damage/cell death, primarily through damage to
the photosystem II reaction center and to oxidation of membrane lipids
(Bowler and Fluhr, 2000 Esterified fatty acid oxidation products in membranes may disturb
membrane integrity and induce plasma leakage. In this respect, esterified F-ring isoprostanoids have been postulated to participate in
membrane leak development due to their remarkably kinked geometry, as
well as the repulsion by the three newly created hydroxy groups and the
adjacent lipophilic fatty acids in the membrane bilayer, leading to
cell death (Morrow et al., 1992 A major source of oxygenated fatty acids in plants appears to be
lipoxygenase acting on free fatty acids. For instance, fatty acid
hydroperoxides were shown to increase from 25 to 335 µg/g of fresh
weight 30 h after application of cryptogein, an established inducer of hypersensitive reaction. It was estimated that 90% of the
total fatty acid hydroperoxides were generated by lipoxygenase, whereas
the remaining 10% represent membrane-bound fatty acid hydroperoxides
(33.5 µg/g of fresh weight) formed by free radical-catalyzed oxidation of membrane lipids simultaneously with the enzymatic process
(Rusterucci et al., 1999 Biological Activity of Isoprostanoids Several isoprostanes have been shown to have potent biological
effects on mammalian tissues. For instance, isoprostanes
F2 act as broncho- and vasoconstrictors in the
nanomolar concentration range, modulate platelet function, contract
lymphatics, and may also induce mitogenesis (for review, see Mueller,
1998 It is notable that phytoprostanes are also structurally related to enzymatically formed linolenate metabolites of the jasmonate-type. Basal levels of phytoprostanes E1 and F1 are generally more than one order of magnitude higher than jasmonic acid levels. However, if phytoprostanes play a role in plant stress physiology has not yet been addressed. This issue remains an exciting challenge for future research.
Preparation of PPF1 and [18O]3PPF1 by Linolenic Acid Autoxidation Linolenic acid (5 g) was dissolved in hexane/diethylether (9:1, v/v), loaded on a silica column (10 g), and eluted with hexane/diethylether (9:1, v/v) to remove any preformed oxygenated fatty acids. The eluate was taken to dryness in a 500-mL round bottom flask and dissolved in 50 mL of carbon tetrachloride. The flask was evaporated in vacuo and filled with 500 mL of oxygen (or oxygen-18 gas, 99.1% atom 18O in the labeling experiment). After stirring the mixture for 10 d at room temperature, the autoxidation mixture was reduced by the addition of 5 g of triphenylphosphine in 50 mL of chloroform and processed as described in "Purification of PPF1." Extraction of PPF1 from Plant Material For analysis of unesterified PPF1, plant material (3 g of fresh weight or 0.3 g of dry weight) was suspended in 20 mL of cold brine containing 0.05% (w/v) of 2,6-di-tert-butyl-4-methylphenol, 20 mg of triphenylphosphine, and 0.2 mL of 1 M citric acid. [18O]3PPF1s (500 ng) were added as an internal standard. After addition of 20 mL of diethyl ether the mixture was homogenized for 3 min with a high performance disperser (Ultra-Turrax T 25, IKA-Werk, Germany) at 24,000 rpm and centrifuged (2,000g, 10 min). The ether phase was removed, taken to dryness under a stream of nitrogen, and dissolved in chloroform. For the determination of total PPF1s (free and esterified), lipids were extracted using a modified Folch procedure. Plant material (1 g of fresh weight or 0.1 g of dry weight) was suspended in 18 mL of methanol/chloroform (2:1, v/v) containing 80 µL of 1 M citric acid, 0.115 mg of 2,6-di-tert-butyl-4-methylphenol, 20 mg of triphenylphospine, and 500 ng of [18O]3PPF1s. After homogenization of the mixture with a high performance disperser for 1 min, 18 mL of chloroform and 8 mL of a 0.88% (w/v) potassium chloride solution were added. The lower organic phase was separated and taken to dryness. The residue was reconstituted in 2 mL of methanol containing 0.1% (w/v) 2,6-di-tert-butyl-4-methylphenol and hydrolyzed after addition of 2 mL of 15% (w/v) KOH at 40°C for 1 h. The reaction was stopped by adding 4 mL of 1 M citric acid and 32 mL of water. Lipids were extracted with diethyl ether, taken to dryness, and reconstituted in 2 mL of chloroform. Purification of PPF1 Linolenic acid (5 g) autoxidation mixture was treated with triphenylphosphine (5 g) for 30 min. The mixture was taken to dryness, reconstituted in 50 mL of chloroform, and loaded on a silica column (4 × 21 cm, 30 g of silica gel 60). The column was washed with 600 mL of diethylether:acetic acid (99:1, v/v) and 300 mL of chloroform:acetone:acetic acid (80:20:1, v/v) to remove remaining linolenic acid, mono-oxygenated linolenate products, and triphenylphosphine. PPF1 were chromatographed isocratically with diethylether:acetone:acetic acid (70:30:1, v/v). Sixty-milliliter fractions of the eluate were taken and aliquots were analyzed by TLC (see below) for the presence of PPF1. PPF1 eluted with 60 to 480 mL of eluent. On an analytical scale, nonesterified PPF1 from plant extracts or linolenate autoxidation mixtures were applied as a chloroform solution to a silica solid-phase extraction column (500 mg). The column was subsequently washed with 6 mL of diethyl ether:acetic acid (98:2, v/v) and 3 mL of chloroform:acetone:acetic acid (80:20:1, v/v). PPF1 were eluted with 6 mL of diethyl ether:methanol:acetic acid (90:10:1, v/v), taken to dryness, and dissolved in 2 mL of methanol. Preparation of PPF1 Standard Solutions A mixture of silica-purified PPF1 was further
purified on a reversed phase HPLC column (LiChrospher 100 RP18e,
5-µm particle size, 8 × 250 mm; Knauer, Berlin, Germany) eluted
with acetonitrile:water:acetic acid (20:80:0.1, v/v) at a flow rate of
3.5 mL/min, and detected at 204 nm (Fig. 3). Fractions of the eluate
were collected and PPF1 isomers were identified by GC-EI-MS
analysis after preparation of the corresponding methyl ester, TMS ether
derivatives. PPF1 isomers eluting under the peaks 1 to 4 (Fig. 3) were each mixed with 500 ng of prostaglandin
F1 TLC Analysis of PPF1 PPF1 and PGF1 Analytical Derivatization Procedures for GC-MS Analysis For GC-EI-MS, silica purified PPF1 were converted to their corresponding methyl esters by treatment with an etheral solution of diazomethane for 5 min. The solution was taken to dryness and silylated with 50 µL of BSTFA in 200 µL of chloroform at 40°C for 30 min. The mixture was taken to dryness and dissolved in hexane for GC-MS analysis. For routine GC- NICI-MS analysis, PPF1 obtained from silica
column purification were derivatized either directly or, in the case of
plant material, after catalytic hydrogenation. For hydrogenation, PPF1 were dissolved in methanol. Adam catalyst (20 mg) was
added and hydrogen gas was bubbled through the sample for 10 min. The sample was filtered, taken to dryness, reconstituted in 200 µL of
chloroform, and derivatized with 10 µL of PFB bromide and 10 µL of
N,N-diethylisopropylamine at 60°C for 30 min. The
mixture was taken to dryness, reconstituted in 2 mL of chloroform, and applied to a silica solid-phase extraction column. The column was
washed with 3 mL of diethyl ether. PPF1 PFB esters were
eluted with 6 mL of diethyl ether:methanol (90:10, v/v). The sample was taken to dryness and TMS ether derivatives were prepared with BSTFA.
For GC-MS analysis, the sample was dissolved in 20 µL of hexane and 1 µL was analyzed. Analyses of phytoprostanes E1
(PPE1) were performed as described (Parchmann and Mueller,
1998 GC-MS GC-NICI-MS was performed using a Varian 3400 gas chromatograph interfaced to a Finnigan MAT quadrupole SSQ 700 mass spectrometer. The MS source was set at 150°C and the electron energy at 70 eV. Isobutane was used as reactant gas when operating the instrument in the NICI mode. PPF1 were analyzed on a 25 m, 0.25-µm film thickness Optima-5 column (Macherey and Nagel, Düren, Germany). The injector was set at 300°C. For analysis of PFB ester, TMS ether derivatives of PPF1, the column temperature was programmed from 175°C to 285°C at 30°C/min and 285°C to 300°C at 2.5°C/min. Methyl ester, TMS ether derivatives of PPF1, were analyzed using a column temperature program from 140°C for 1 min, 140°C to 235°C at 20°C/min, 235°C to 250°C at 1°C/min, and 250°C to 300°C at 30°C/min.
Received February 22, 2000; accepted July 13, 2000. 1 This work was supported by the Sonderforschungsbereich 369 of the Deutsche Forschungsgemeinschaft, Bonn.
* Corresponding author; e-mail Martin.Mueller{at}botanik.uni-wuerzburg.de; fax 49-931-888-6182.
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