1. Introduction
Flowers are the reproductive organs of angiosperms and have the task of facilitating sexual reproduction. To attract pollinators, they produce bright colours and volatile compounds together with abundant pollen and nectar, which are the reward for pollinators attracted by the colours and fragrant compounds. However, florivores are also attracted, and in some cases discouraged by the emission of particular combinations of volatile compounds [
1].
In addition, it is an ancient custom to use flowers as food, a tradition that has recently gained new considerable popularity not only because of the particular taste and smell but also because of the beneficial components for human health present [
2]; confirming this a paper by Demasi et al. [
3] on the conservation of edible flowers was chosen as the cover story of the July 2021 issue of
Horticulturae.
The species of the genus
Pelargonium are most famous for the essential oils extracted from their fragrant leaves and for their ornamental value. The interest in
Pelargonium plants is due to their varied and intense scents including rose, nutmeg, green apple, coconut, almond, lemon, peppermint and strawberry. ‘Scented
Pelargonium’ (historically scented geraniums) indicates a group of aromatic plants in which the leaves and flowers have many uses in recipes, aromatherapy, herbal and medicinal preparations [
4,
5,
6].
Pelargonium flowers are little studied although some of them, e.g., flowers of
P. graveolens,
P. tomentosum,
P. odoratissium and
P. fragrans are included in various recipes, especially sweet ones, and are marketed as edible flowers [
7]. The
Pelargonium cultivar ’Endsleigh’ (lavender scented) has long been considered a variety originating from a cross between
Pelargonium capitatum (hexaploid 2n = 66) and
Pelargonium quercifolium (tetraploid 2n = 44) [
8]. This plant has strongly scented spicy leaves which can be used to add a mixed spice flavour to cooking and makes a great long-lasting potpourri [
9].
Plant volatile organic compounds (VOCs) are involved in essential biological functions such as defence against herbivorous predators and pathogens, attraction of pollinating insects and seed dispersal [
10] while some components determine aromatic characteristics which are employed to add flavour to food playing an important role in the acceptability of products by consumers [
11].
Therefore, we decided to study the VOCs produced by the flowers of Pelargonium ’Endsleigh’ during the flowering process (mature bud, full bloom, senescing) by the whole flower and its parts (sepals, petals, stamens and carpels) in order to identify the chemical compounds produced and which part of the flower is most active in the production of VOCs. In addition, both the phytochemical profile and the antioxidant activity of the flowers were examined.
2. Materials and Methods
Fresh
Pelargonium ’Endsleigh’ flowers were harvested at three stages of development: mature bud, full bloom and senescing (
Figure 1) and analysed as such or after separation into sepals, petals and stamens/pistils (
Figure 2). The dry weight was determined by placing the flowers in an oven at a temperature of 105 °C to constant weight.
The analysis of volatile compounds was carried out by solid-phase micro extraction (SPME) methodology. Approximately 1 g (FW) of flowers was sealed into 20-mL SPME vials (Agilent Technologies, Palo Alto, CA, USA) by metal screw-caps with pre-notched Teflon silicone septa. The vials were then placed at 40 °C for 5 min in a thermostatically controlled bath to allow the evaporation of the compounds; hereafter, a SPME syringe was inserted and the fibre (50/30 µm Divinylbenzene/Carboxen/Polydimethylsiloxane, Supelco/Merck KGaA, Darmstadt, Germany), which was previously conditioned for 5 min at 235 °C in the gas chromatograph injector, was exposed for 10 min to absorb the volatile compounds. Subsequently, the fibre was inserted into the injector port of a gas chromatography with a mass spectrometry detector (Agilent 7890B coupled with MS single quadripole Agilent 5977A) and the desorption of the volatile compounds was performed at 235 °C for 4 min. The injector was operated under spitless mode. At this point, the chromatographic run was started with an Agilent HP-5ms column (30 m × 0.25 mm, 0.25 μm) (which temperature was raised from 60 °C to 250 °C with a constant increase of 3 °C/min) with a constant helium (purity > 99.999%) flow of 1.0 mL/min. Compounds were identified by library search and/or analytical standard if available. The mass spectrum of an unknown compound was searched in data processing system [
12]. Substances with a score above 800, both in terms of identity and purity, were considered to be identified after comparing the detected compound with the one in the NIST Computational Chemistry Comparison and Benchmark database [
12]. Retention index (RI) was obtained essentially as reported by Zhao et al. [
13] employing as reference the retention times of a series of C
8-C
20 alkanes separated under the GC-MS conditions mentioned above, and applying the following formula:
where,
ta is the retention time of the unknown peak
a;
tn the retention time of
n-alkane
Cn; and
tn+1 the retention time of
n-alkane
Cn+1;
n = carbon number of the alkane which elutes before the unknown peak
a.
The semi-quantitative analysis of volatile compounds was carried out as reported by Zhao et al. [
13] with some modifications. The compound 1,7,7-trimethylbiciclo [2.2.1] 2-heptanone was chosen as the internal standard; 2 μL of a solution 1.25 μg/mL of internal standard in hexane were added to the samples. The calculation of the amount of VOCs was determined with the following formula: Qc = (Qs × Ac)/As where Qc is the amount of VOC in the sample, Qs the amount of standard, Ac the area of the VOC in the sample and As the area of the standard.
Phenolic and organic compound characterization. Samples finely powdered with mortar and pestle in presence of liquid nitrogen were extracted in a ratio of 1:20 FW/V with methanol:water (75:25) acidified with formic acid 0.1% for 30 min in constant agitation. The extract was centrifuged, and the extraction was repeated on the pellet. The supernatants were mixed and evaporated, then resuspended with high performance liquid chromatography (HPLC) water acidified with 0.1% formic acid.
The total phenolic content (TPC) was determined using the spectrophotometric Folin-Ciocalteau method [
14], the absorbance was measured after a 1:10 dilution with a JASCO V-550 UV/VIS spectrophotometer at 765 nm, and data were expressed as mg of gallic acid equivalent (GAE) per g dry weight (DW).
Compound characterization was performed by an Agilent 1200 Liquid Chromatography system (Agilent Technologies, Palo Alto, CA, USA) equipped with a standard autosampler. The HPLC column was an Agilent Extended C18 (1.8 μm, 2.1 × 50 mm). Separation was carried out at 40 °C with a gradient elution program at a flowrate of 0.5 mL/min. The mobile phases consisted of water plus 0.1% formic acid (A) and acetonitrile (B). The following multistep linear gradient was applied: 0 min, 5% B; 13 min, 25% B; 19 min, 40% B. The injection volume in the HPLC system was 5 µL. The HPLC system was coupled to a DAD (Agilent Technologies) set at 280 nm and an Agilent 6320 TOF mass spectrometer equipped with a dual electrospray ionization (ESI) inter-face (Agilent Technologies) operating in negative ion mode. Detection was carried out within a mass range of 50–1700
m/z. Accurate measurements of the mass corresponding to each total ionic current (TIC) peak were obtained with a pump (Agilent G1310B) introducing a low flow (20 μL/min) of a calibration solution containing internal reference masses at
m/z 112.9856, 301.9981, 601.9790, 1033.9881, and using a dual nebulizer ESI source in negative ion mode [
15]. Other mass spectrometer conditions were as follows: capillary voltage 3.0 kV in negative mode; nitrogen was used as the nebulizer and desolvation gas; drying gas temperature: 300 °C; drying gas flow: 12 L/min, nebulizing gas pressure: 40 psig; finally, the source temperature was 120 °C. Mass Hunter software (Agilent Technologies, Palo Alto, CA, USA) was used to process the mass data of the molecular ions.
The compounds were quantified using calibration curves of authentic standards myricetin, kaempferol, quercetin purchase from Merck Life Science (Milano, Italy), while Myricetin 3-O-glucoside, Kaempferol 3-O-galactoside and Kaempferol 3-O-glucoside were employed for the identification of chemical compounds after HPLC/MS analysis.
The evaluation of the antioxidant activity was carried out by testing three aspects: scavenger, reducing and quenching capacity.
DPPH Assay. Antioxidant activity was determined in vitro by evaluation of the free radical scavenging activity using 2,2-diphenyl-1-picrylhydrazyl (DPPH•) (DPPH assay) [
16]. Inhibition of free radical DPPH• was expressed as Trolox (6-hydroxy-2,5,7,8-tetra-methylchroman-2-carboxylic acid) equivalents (TE) per g DW.
Ferric Reducing Antioxidant Power (FRAP). The ferric reducing ability was deter-mined by the FRAP method [
17]. The absorption of the reaction mixture was measured at 593 nm using Perkin Elmer 2030 Multilabel reader Victor X5 after 3 min of incubation at 37 °C. The samples were measured in triplicate, and the FRAP was expressed as Trolox equivalents (TE)/g DW.
Superoxide anion scavenging activity assay. The assay was carried out according to Beauchamp and Fridovich [
18]. The photo-induced reactions were performed using fluorescent lamps (200 W at 1 m). All samples were measured in triplicate, and the superoxide anion scavenging activity was expressed as g DW corresponding to half maximal inhibitory concentration (IC
50).
All data were reported as the mean ± standard deviation (SD), with at least three replications for each sample. Statistical evaluation was conducted by Duncan’s test to discriminate among the mean values. All statistical analyses were performed using the software Statistica (StatSoft, Tulsa, OK, USA).
4. Discussion
A relatively low number of compounds have been detected in extracts obtained from the floral tissues of
P. ‘Endsleigh’ flowers; we have identified approximately the same number of flavonoids as Boukhris et al. [
28] in leaves and flowers of
P. graveolens, but far fewer than the 40 compounds found by Marchioni et al. [
29] in
Pelargonium odoratissimum ‘Lemon’ or of over 50 compounds identified in the flowers of
P. endliclerianum [
30]. Few metabolites are in common with the flower of
Geranium sylvaticum [
22] but those shared kaempferol, quercetin and myricetin methyl ethers, are known to function as defensive compounds against herbivorous insects [
31].
The level of total phenolic compounds was significant; the reported values are similar to those of flowers of
P. odoratissimum [
29] in which TPC content was the highest among the flowers of the four species analysed, and approximately 40% and 50% higher than that one of the flowers of
Geranium sylvaticum [
32] and
P. graveolens flowers [
28], respectively. Comparing with literature regarding edible flowers, the TPC content results 50% higher than the best of the 26 flowers analysed by Demasi et al. [
33] and within the range of values reported by Janarny et al. [
34] for Sri Lankan edible flowers.
The antioxidant activity, slightly higher at the stage of full bloom for
P. ‘Endsleigh’, was not in accordance with the phenols content, but it was more or less in line with previous results [
28,
33,
34] despite the fact that authors use different units of measure. It would be advisable for all authors to express the values as a function of the original dry weight of the sample/plant organ.
There is very little work on the volatile compounds emitted by Geraniaceae flowers, hence it is only possible to compare data with Bozan et al. [
30] (
P. endliclerianum), Cao et al. [
35] (
P. hortorum), and Marchioni et al. [
29] (
P. odoratissimum). The major volatiles of
P. endliclerianum flowers were Germacrene D (27.11%), β-Caryophyllene (11.34%), α-Phellandrene (9.79%), α-Pinene (4.89%) [
30]; for
P. hortorum Zingiberene (29.88%), α-Longipinene (26.65%), β-Myrcene (11.07%) and 3-Hexen-1-ol (5.39%) [
35]; for the
P. odoratissimum the two most present compounds were again Germacrene D (27.03%) and β-Caryophyllene (23.23%), followed in order by (
E)-
β-Farnesene (9.63%) and α-Humulene (5.21%) [
29].
Table 5 shows instead the main volatiles of the
P. ‘Endsleigh’ flowers at full bloom are different: the two major compounds are Guaia-6-9 diene (54.99%), and 3-Carene (11.25%), followed by β-Caryophyllene (5.49%) and Cadina-1(10),4-diene (4.70%), with Germacrene D only at 1.43%. These data clearly indicate that the flowers of the different
Pelargonium species produce both a remarkable variety of odour compounds and also varying combinations of the volatile compounds. In addition, the ratios between the various VOCs change slightly in the case of petals for which there is a greater presence of β-Caryophyllene than 3-Carene, 9.35% compared with 7.19%, respectively.
Then, in the case of
P. ‘Endsleigh’ flowers the smells perceived by humans should be different from the other investigated
Pelargonium flowers releasing mostly woody odours (sesquiterpenes with Guaiane Skeleton as Guaia-6-9 diene) [
36], plus a sweet, turpentine/pine resin-like odour (3-Carene) [
37], with a minor scent midway between odour of cloves and turpentine (β-Caryophyllene) [
37] and of thyme herbal woody dry (Cadina-1(10),4-diene) [
38]. Anyway, of the major
P. ‘Endsleigh’ flower VOCs only 3-Carene increase significantly during the flower development whereas α-Copaene (woody spicy odour), which is the second most abundant VOC after Guaia-6-9 diene at mature bud stage falls in percentage terms from approximately 7% to less of 2% during the flower development (
Table 5). In order to understand the meaning of these variations in VOCs production, it is necessary for the scientific community to produce more data regarding the ecological role of these chemical compounds to be included later in The Pherobase [
39] which is already a useful reference. For instance, α-copaene is a minor component but also a natural kairomone of
Ceratitis capitata, a potent attractant for male of Mediterranean fruit flies [
40] and it is produced by hundreds of flowers of different species [
39].
In order to understand which floral organs produce VOCs, we have analysed sepals, petals and stamens/pistils separately. The result, compared to an identical fresh weight, was somewhat surprising as it was assumed that it was mainly the petals that emitted volatile compounds as e.g., the yield in phenols and flavonoids was higher in petals of
Geranium sylvaticum [
32]. On the contrary, as the scales of
Figure 4,
Figure 5 and
Figure 6 show, it is the sepals that produce a complex mixture of VOCs and in greater quantity than the other organs.
Previously, other authors have demonstrated that monoterpenes are emitted mostly from rose petals [
41] and that peaking of floral fragrance in mature flowers enhances pollination efficiency [
42,
43]. In
Rosa damascena, the main volatiles increase in the early stage flower development, peak in a second stage, decreasing thereafter [
44]. Li et al. [
45] for
Luculia pinceana considered four stages of flower development (bud, initial-flowering, full-flowering and end-flower) showing that floral scent emission had its peak level at the initial-flowering stage; an identical result was obtained one year later by the same group for
Luculia yunnanensis flowers [
46]. In the case of tepals of
Magnolia denudata the highest amount of volatiles and strongest aroma intensity are at the semi open stage [
47]. Instead, Yu et al. [
48] monitored volatile organic compounds emitted from
Jasminum sambac ‘Bifoliatum’ flowers at five developmental stages (closed bud stage, start opening, opening, fully opened, start senescence) demonstrating a higher production of volatiles at flower opening. On the contrary, the flowers of the orchid
Phalaenopsis bellina emit volatiles mainly at the stage of full bloom (3 stages: flower bud, partial bloom, full bloom) [
49]; a similar result was also obtained by Bera et al. [
50] for
Zygopetalum maculatum.