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Essential oils of Pinus nigra J.F. Arnold subsp. laricio Maire: Chemical composition and study of their herbicidal potential
⁎Corresponding author at: Faculté des Sciences de Bizerte, Université de Carthage, Bizerte, Tunisia. Tel.: +216 96137094. amri_amri@live.fr (Ismail Amri)
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Received: ,
Accepted: ,
This article was originally published by Elsevier and was migrated to Scientific Scholar after the change of Publisher.
Peer review under responsibility of King Saud University.

Abstract
The chemical composition of essential oils isolated by hydrodistillation from the needles of Tunisian Pinus nigra L. subsp. laricio was analyzed by GC and GC/MS. 27 compounds were identified, representing 97.9% of total oil, which was found to be rich in oxygenated diterpenes (38.5%) particularly manool oxide (38%) and sesquiterpene hydrocarbons (41.4%) that included germacrene D (16.7%), δ-cadinene (9%) and (E)-caryophyllene (8.9%). Results of the herbicidal effects of the oil when tested on Phalaris canariensis L., Trifolium campestre Schreb. and Sinapis arvensis L., indicated that the oil completely inhibited germination and seedling growth at a high concentration (5 μL/mL−1), while at low doses the oil acted by decreasing germination and partially inhibiting seedling growth of all tested weeds.
Keywords
Pinus nigra subsp. laricio
Essential oil
Weeds
Phytotoxicity
1 Introduction
Allelopathy is the science that studies processes in which secondary metabolites from plants and microorganisms are involved, affecting growth and development of biological systems (Qiming et al., 2006). The use of secondary metabolites implicated in allelopathic interactions as sources for news agrochemical models could satisfy the requirements for crop protection and weed management (Singh et al., 2003). Weeds may be defined as plants with little economic value and possessing the potential to colonize disturbed habitats or those modified by human activities. According to an estimate, in US alone, weeds cause a loss on the crop production in the range of 12% (Pimentel et al., 2001). As per Agrow report, the total value of world’s agrochemical market was between US$31–35 billion and among the products herbicides accounted for 48% followed by fungicides (22%) (Agrow, 2007). However, the excessive use of synthetic pesticides in the croplands, urban environment, and water bodies to get rid of noxious pests has resulted in an increased risk of pesticide resistance, enhanced pest resurgence, toxicological implications to human health and increased environmental pollution (Gupta and Bhattacharya, 2008; Hong et al., 2009). In an attempt to reduce the use of synthetic pesticides, extensive investigations into the possible exploitation of plant compounds as natural commercial products, that are safe for humans and the environment were made. Indeed, the search for natural compounds and management methods as alternatives to classical pesticides has become an intense and productive research field (Zanie et al., 2008; Dudai et al., 1999). Recently there has been considerable interest in biologically active compounds from plants as sources of bio-pesticides. Essential oils from aromatic plants are examples of compounds with potential to control pests; they are becoming more popular because many synthetic drugs are connected with unpleasant side effects. Volatile oils also represent an interesting alternative due to emerging resistance pests against synthetic agents (Singh et al., 2003). The phytotoxic potential of essential oils and their pure components have also been studied; in fact, earlier studies have documented that those volatile oils and their constituents inhibit, delay seed germination and inhibit seedling growth of many weeds and cultivated crops (De Feo et al., 2002). The growth inhibitory activity of plant essential oils has tremendously increased the interest in exploring volatile oil from aromatic plants for potential weed management (Singh et al., 2003). Such studies are important in view of the environmental and human health concerns, and increasing herbicidal resistance linked to synthetic herbicides; thus, there is a need to search for environmentally safer and novel compounds with weed suppressing ability (De Feo et al., 2002).
Pinus nigra J.F. Arnold subsp. laricio Maire is a conifer tree of the genus Pinus, family Pinaceae. There are about 115 pine species, which are divided into three subgenera, based on cone, seed and leaf characters (Macig et al., 2007). Pines are among the most important commercial species used for timber and wood pulp in temperate and tropical regions of the world. Pines species were known for their richness in essential oils. The volatile compounds from the needles of P. nigra have been investigated in Turkey, Italy and Corsica (Rezzi et al., 2001; Macchioni et al., 2003; Sezik et al., 2010), but to the best of our knowledge, there is no report about the chemical composition and herbicidal activity of essential oils from P. nigra ssp. laricio grown in Tunisia. Therefore the aims of this work were to assay the main constituents of the essential oil obtained from Tunisian P. nigra subsp. laricio, and to assess their herbicidal activity against germination and seedling growth of three common weeds.
2 Materials and methods
2.1 Plant material
The needles of 50 year old P. nigra J.F. Arnold subsp. laricio Maire were collected during October 2009 (autumn season) from the Souinet arboreta of the National Institute of Researches on Rural Engineering, Water and Forests. Five samples collected from more than 5 different trees were harvested and mixed for homogenization. The experimental site is located in Ain Draham, in the north of Tunisia at an altitude of 492 m, where humid climate prevails. The voucher specimen of the plant (No. Pn.950) was prepared and deposited at the herbarium division of the Institute.
2.2 Isolation of the essential oils
Three replications of 100 g of air-dried and finely grounded raw materials were submitted to hydrodistillation for 5 h with 500 mL distilled water using a Clevenger type apparatus according to the European Pharmacopoeia (2004). The oil obtained was collected and dried over anhydrous sodium sulfate and stored in sealed glass vials in a refrigerator at 4 °C prior to analysis. Yield based on dry weight of the sample was calculated (w/w%).
2.3 Gas chromatography analysis/mass spectrometry analysis conditions
2.3.1 Gas chromatography analysis
The essential oils were analyzed using a Hewlett Packard 5890 II GC equipped with Flame Ionization Detector (FID) and HP-5 MS capillary column (5% phenyl/95% dimethylpolysiloxane: 30 m × 0.25 mm id, film thickness 0.25 μm). Injector and detector temperature were set at 250 °C and 280 °C, respectively. Oven temperature was kept at 50 °C for 1 min then gradually raised to 250 °C at 5 °C/min−1 and subsequently, held isothermal for 4 min. Nitrogen was the carrier gas at a flow rate of 1.2 mL/min−1. Diluted samples (1/100 in hexane, v/v) of 1.0 μL were injected manually and in the splitless mode. Quantitative data were obtained electronically from FID area percent data without the use of correction factors.
2.3.2 Gas chromatography analysis/mass spectrometry analysis
For GC/MS detection, an electron ionization system, with ionization energy of 70 eV, a scan time of 1.5 s and mass range 40–300 amu, was used. Helium was the carrier gas at a flow rate of 1.2 mL/min. Injector and transfer line temperatures were set at 250 and 280 °C, respectively. Oven program temperature was the same with GC analysis. Diluted samples (1/10 in hexane, v/v) of 1.0 μL were injected manually and in the splitless mode. The identification of the compounds was based on mass spectra (compared with Wiley 275.L, 6th edition mass spectral library) or with authentic compounds and confirmed by comparison of their retention indices either with those of authentic compounds or with data published in the literature as described by Adams (2001). Further confirmation was done from Retention Index data generated from a series of n-alkanes retention indices (relative to C9–C28 on the HP-5 MS capillary column).
2.3.3 Seed germination and seedling growth experiments
Mature seeds of annual weeds Phalaris canariensis L., Trifolium campestre Schreb. and Sinapis arvensis L. were collected from parent plants growing in fields of Tunisia area, in July 2009. The plants were dried for 15 days at room temperature, afterward the seeds were extracted. Uniform healthy seeds were selected and stored at 4 °C until germination tests. To avoid possible inhibition caused by toxins in fungi or bacteria, the seeds were sterilized with 15% sodium hypochlorite for 20 min. They were then rinsed with abundant distilled water. Empty and undeveloped seeds were discarded by floating in tap water and the remaining seeds were used. To study herbicidal effect of the essential oil, the oil was dissolved in tween-water solution (0.1%; v/v). Six milliliters of the appropriate essential oil solution was transferred to a Petri dish placed on the bottom of which were 2 layers of filter paper to obtain the final concentration of the treatment (0, 1, 2, 3, 4 and 5 μL/mL−1). Afterward, 20 seeds were placed and distributed evenly on the filter paper. Petri dishes were closed with an adhesive tape to prevent escaping of volatile compounds and were kept at 25 °C on a growth chamber supplied with 12 h of fluorescent light (Amri et al., 2011). The number of germinated seeds and seedling lengths were measured after 10 days. The treatments were arranged in a completely randomized design with three replications including controls.
2.4 Statistical analysis
Data obtained from essential oil analysis, seed germination and seedling growth assays were expressed as mean values and were subjected to one-way analysis of variance (ANOVA), using the SPSS 13.0 software package. Differences between means were tested through Student–Newman–Keuls (SNK) and values of p ⩽ 0.05 were considered significantly different.
3 Results and discussion
3.1 Chemical composition
The hydro-distillation of dried P. nigra ssp. laricio needles gave a yellowish essential oil (yields 0.6%, w/w). The qualitative and quantitative analytical results of identified compounds by GC and GC–MS are shown in Table 1. Twenty-seven constituents accounting for 97.9% of total oil composition were identified. The oil was dominated by oxygenated diterpenes (38%) and sesquiterpenes hydrocarbons (41.4%) but monoterpenes were represented by a small quantity (10.5%). The major components were manool oxide (38%), germacrene D (16.7%), δ-cadinene (9%), (E)-caryophyllene (8.9%), α-cadinol (4.3%), limonene (2.6%), α-pinene (2.1%) and other components which are present in appreciable amounts. To the best of our knowledge, there are many reports on the chemical composition of P. nigra essential oils. On the other hand, our results were different from the literature by the low amounts of α and β-pinene and the high levels of 13-epi-manool oxide. The chemical composition of P. nigra ssp. dalmatica essential oil from needles was previously investigated by Chalchat and Gorunovic in Italy (Chalchat and Gorunovic, 1995). They found α-pinene, borneol and (E)-caryophyllene as the major compounds. In Turkey, α-pinene (22.2–43.18%), β-pinene (22.4–34.1%), germacrene D (6.45–14.9%) and (E)-caryophyllene (5.65–9.21%) were considered to be the major components of essential oils of P. nigra Arnold (Sezik et al., 2010). Essential oil of P. nigra Arnold from central Italy was studied by Macchioni et al. (2003), with α-pinene, germacrene D, (E)-caryophyllene and β-pinene as the major compounds. But, the chemical composition from our essential oil shows similarity with P. nigra ssp. laricio of Corsica with α-pinene, manool oxide, germacrene D, β-myrcene, (E)-caryophyllene and limonene were found to be the main constituents (Rezzi et al. 2001). This is the first report which indicates that manool oxide is the major component in the essential oil from P. nigra ssp. laricio cultivated in Tunisia. The above results suggest that the great variations in the chemical composition of the essential oil from P. nigra grown in Tunisia and those from other countries may be due to many factors such as subspecies (laricio and dalmatica), geographic factors, genetic background of tree, harvest time and extraction method.
| Peaks | Compounds | RI | Area % | Identification |
|---|---|---|---|---|
| 1 | α-Pinene | 939 | 2.1 ± 0.1 | RI, MS, Co-inj |
| 2 | β-Pinene | 979 | 0.4 ± 0.4 | RI, MS |
| 3 | β-Myrcene | 990 | 0.8 ± 0.3 | RI, MS, Co-inj |
| 4 | δ-3-Carene | 1011 | 0.3 ± 0.3 | RI, MS, Co-inj |
| 5 | Limonene | 1029 | 2.6 ± 0.5 | RI, MS |
| 6 | γ-Terpinene | 1059 | 0.8 ± 0.3 | RI, MS |
| 7 | Terpinolene | 1088 | 0.2 ± 0.2 | RI, MS, Co-inj |
| 8 | Linalool | 1096 | 0.1 ± 0 | RI, MS |
| 9 | α-Terpineol | 1188 | 2.3 ± 0.5 | RI, MS |
| 10 | Linalool acetate | 1257 | 2 ± 0.5 | RI, MS |
| 11 | Isobornyl acetate | 1285 | 0.1 ± 0 | RI, MS |
| 12 | α-Copaene | 1376 | 0.3 ± 0.1 | RI, MS |
| 13 | β-Cubebene | 1388 | 0.1 ± 0.1 | RI, MS |
| 14 | (E)-caryophyllene | 1419 | 8.9 ± 1.1 | RI, MS, Co-inj |
| 15 | α-Humulene | 1454 | 2 ± 0.2 | RI, MS, Co-inj |
| 16 | (E)-β-farnasene | 1456 | 0.2 ± 0 | RI, MS |
| 17 | α-amorphene | 1484 | 2.4 ± 0.6 | RI, MS |
| 18 | Germacrene D | 1485 | 16.7 ± 1 | RI, MS |
| 19 | α-muurolene | 1500 | 1.8 ± 0.6 | RI, MS |
| 20 | Germacrene A | 1509 | 0.1 ± 0.1 | RI, MS |
| 21 | δ-Cadinene | 1523 | 9 ± 0.9 | RI, MS |
| 22 | (E)-nerolidiol | 1563 | 0.5 ± 0.2 | RI, MS |
| 23 | Caryophyllene oxide | 1583 | 2.1 ± 0.1 | RI, MS |
| 24 | α-Cadinol | 1654 | 4.3 ± 0.5 | RI, MS |
| 25 | (2E, 6E)-farnesyl acetate | 1846 | 0.4 ± 0.1 | RI, MS |
| 26 | Manool oxide | 1987 | 38 ± 1.9 | RI, MS |
| 27 | Thumbergol | 2046 | 0.5 ± 0.3 | RI, MS |
| Yield (w/w) % | 0.6 ± 0.1 | |||
| Total identified % | 97.9 ± 1.3 | |||
| Monoterpenes hydrocarbons % | 7 ± 0.9 | |||
| Oxygenated monoterpenes % | 3.4 ± 0.8 | |||
| Sesquiterpenes hydrocarbons % | 41.4 ± 1.2 | |||
| Oxygenated sesquiterpenes % | 7.4 ± 0.1 | |||
| Oxygenated diterpenes % | 38.5 ± 1.8 | |||
RI: Retention Index on apolar HP-5 column.
MS: mass spectrometry.
Area%: percentage calculated by GC-FID on apolar HP-5 column.
MI: methods of identification.
Co-inj: co-injection.
3.2 Herbicidal effects of the oil on weed germination and seedling growth
The phytotoxic effects of P. nigra oil were tested on seed germination and seedling growth of S. arvensis, T. campestre and P. canariensis, common weeds in Tunisia. Table 2 shows that essential oil strongly inhibited the germination and seedling growth of tested weeds in a dose dependent manner with the effect being significantly more effective on S. arvensis than T. campestre and P. canariensis. Indeed, at lower concentrations from 1 to 3 μL/mL−1 for S. arvensis and from 1 to 4 μL/mL−1 for T. campestre and P. canariensis, the germination and seedling growth of weeds were partially reduced. However, at high concentrations (4 μL/mL−1 for S. arvensis and 5 μL/mL−1 for T. campestre and P. canariensis), the germination and seedling growth of all tested weeds were totally inhibited. These results are in agreement with literature (Vokou et al., 2003; De Martino et al., 2010; Amri et al., 2011, 2012). Indeed, in recent reports, we have shown the herbicidal effects of some species essential oils belonging different families that Pinaceae, (Amri et al., 2011, 2012, 2013). According to these studies, Pine species were shown to possess a potent herbicidal activity, recently, it has been demonstrated that Pinus taeda, Pinus pinea, Pinus halepensis and Pinus patula displayed inhibitory effects against the germination and seedling growth of weeds and cultivated crops (Amri et al., 2011, 2012, 2013; Kennedy et al., 2011), also. Our data agree with the literature on the inhibitory activity exerted by essential oils against weed germination and seedling growth of weeds and cultivated crops and their phytotoxicity was generally attributed to the allelopathic potential of some terpenes (Vokou et al., 2003; De Martino et al., 2010). It has been shown that the herbicidal effects of essential oils resulted from the combined reactions of several compounds including addition, synergetic and antagonistic (Vokou et al., 2003). Looking at the chemical composition of the oil (Table 1) of P. nigra, it is shown that more than 11 compounds are known to have herbicidal activity; α-pinene, β-pinene, β-myrcene, limonene, δ-3-carene and γ-terpinene are six hydrocarbonated monoterpenes that are present in our oil, indeed, these compounds have been reported to have herbicidal activities (Vokou et al., 2003; De Martino et al., 2010). Linalool and α-terpineol are two oxygenated monoterpene alcohols, linalyl acetate and isobornyl acetate are two esters; these compounds are present in the oil of P. nigra in different percentages and they are known for their potential herbicidal activity (Vokou et al., 2003).
| Weeds | Dose (μL/mL−1) | Germination (%) | Seedling growth (mm) | |
|---|---|---|---|---|
| Aerial parts | Roots | |||
| S. arvensis | 0 | 95 ± 5 a | 12.3 ± 1 a | 11.9 ± 1 a |
| 1 | 63.3 ± 2.9 b | 9.2 ± 1 b | 7.2 ± 1 b | |
| 2 | 38.3 ± 7.6 c | 5.8 ± 1.4 c | 4.2 ± 1 c | |
| 3 | 20 ± 5 d | 2.5 ± 0.5 d | 1.2 ± 0.7 d | |
| 4 | 0 ± 0 e | 0 ± 0 e | 0 ± 0 d | |
| 5 | 0 ± 0 e | 0 ± 0 e | 0 ± 0 e | |
| T. campestre | 0 | 85 ± 5 a | 13 ± 1 a | 12.1 ± 1 a |
| 1 | 81.7 ± 7.6 a | 12 ± 1 a | 8.2 ± 1 b | |
| 2 | 60 ± 5b | 7.2 ± 1 b | 3.5 ± 0.4 c | |
| 3 | 41.7 ± 2.9 c | 5.5 ± 0.5 c | 2.4 ± 0.3 cd | |
| 4 | 13.3 ± 2.9 d | 1.8 ± 0.8 d | 1.4 ± 0.4 d | |
| 5 | 0 ± 0 e | 0 ± 0 e | 0 ± 0 e | |
| P. canariensis | 0 | 93.3 ± 5.8 a | 12.7 ± 1.1 a | 11.1 ± 0.6 a |
| 1 | 73.3 ± 5.8 b | 10.3 ± 1.2 b | 7.9 ± 1 b | |
| 2 | 66.7 ± 7.6 b | 7.2 ± 1.2 c | 5.9 ± 0.8 c | |
| 3 | 50 ± 5 c | 3.5 ± 0.5 d | 4.2 ± 0.3 d | |
| 4 | 21.7 ± 2.9 d | 1.6 ± 0.5 e | 2.3 ± 0.6 e | |
| 5 | 0 ± 0 e | 0 ± 0 e | 0 ± 0 e | |
Means in the same column with the same letter are not significantly different at p ⩽ 0.05.
In addition, in our study, the oil was rich in sesquiterpenes (E)-caryophyllene and manool oxide (oxygenated diterpene) which are known for their phytotoxic effects (De Feo et al., 2002; Singh et al., 2006). Numerous studies showed the phytotoxic potential of essential oil isolated from different plants. Singh et al. (2006) have demonstrated that exposure of seedling to α-pinene inhibited seedling growth causing oxidative damage in the root tissue. Kil et al. (2000) reported that (E)-caryophyllene was an important sesquiterpene of essential oil of Artemisia lavandulaefolia, which suppressed the seedling growth of Achyranthes japonica; Wang et al. (2009) showed that (E)-caryophyllene at the dose of 3 mg/L significantly inhibited the germination rates and seedling growth of Brassica campestris and Raphanus sativus. Generally, both monoterpenoids and sesquiterpenoids appear to be involved in these allelopathic interactions, for this reason the herbicidal activity of our oil was attributed to the presence of both sesquiterpenes and monoterpenes and the synergism between components does play an important role. Although the exact mechanisms of essential oil on germination and seedling growth inhibition remain unclear however, such inhibitory effects could be caused by allelochemicals interfering with physiological and biochemical processes in target species (Weir et al., 2004; Blanco, 2007).
4 Conclusion
According to our knowledge, this is the first report regarding P. nigra subsp. laricio essential oil herbicidal activity. The development of natural pesticides would help to decrease the negative impact of synthetic agents such as residues, resistance and environmental pollution (Dudai et al., 1999) In this respect, essential oils, as natural herbicides, present two main characters: the first is their natural origin which means more safety to the people and the environment, and the second is that they have be considered at low risk for resistance development by weeds (Vokou et al., 2003). It is believed that it is difficult to develop resistance to such a mixture of oil components with apparently different mechanisms of action (Vokou et al., 2003). Based on our preliminary results, the essential oils of P. nigra subsp. laricio could be suggested as alternative herbicides. However, further studies are required to determine the cost, applicability, safety and phytotoxicity against the cultured plants of these agents as potential herbicide.
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