The genus
Türkiye is the main supplier of Mediterranean oregano contributing to over 90% of oregano exports. A total of 16 756 t of oregano were exported in 2019 from Türkiye (Karlı et al., 2020). Moreover, Türkiye provides 70% of the world demand for oregano oil, and 66 t of oregano oil was exported in 2018 (Bejar, 2019). To satisfy the regional and international demand, the plant sources are being harvested in increasing volumes and largely from wild populations in Türkiye. Intensive collection from nature has a detrimental impact on the structure and dynamics of the harvested plant populations, and these medicinal and aromatic plants are not of standard quality (Katar et al., 2022). Since commercial value of oregano depends on the content and composition, cultivated oregano growing has been accelerated recently (Kutlu et al., 2019). The yield and quality of oregano are affected by the mineral composition of the soil, fertilization, frequency of irrigation and water quality. Inadequate and imbalanced nutrient conditions in oregano cultivation lead to a decrease in herb and essential oil (EO) yield, while adequate supply of nutrients can result in huge synthesis of phenolic and flavonoid compounds in oregano (Çolak Esetlili and Çakıcı, 2010). Chemical fertilizers are widely used to increase crop yield and quality. Medicinal plants must be natural and harmless; they should not react or contaminate with pesticides, heavy metals and toxic chemicals in order to remain compliant with international standards. But conventional farming may not meet all these safety requirements (Kosakowska et al., 2021). Furthermore, organic products are accepted in the global market and fetch the best prices as compared with those grown with conventional farming (Cilak et al., 2021). Research studies focussing on the use of organic fertilizer in medicinal and aromatic plants growing (Naguib et al., 2012) reported positive effects on herb yield, nutrient content, EO content and quality such as
Studies on the effects of fertilization on
The study was conducted from 2019 to 2021 in the field of Bati Akdeniz Agricultural Research Institute (36.56°N, 30.53°E, and altitude 28), Türkiye. The monthly average air temperature and rainfall values of trial years are given in Table 1. According to the climatic data, the average temperature in 3 years was 19.2, 19.3 and 19.5 °C, respectively. The total rainfall was 1 097.0 842.0 and 1 062.0 mm according to the respective years (Anonymous, 2023).
Meteorological data of the experiment years.
Months | Total precipitation (mm) | Mean temperature (°C) | ||||||
---|---|---|---|---|---|---|---|---|
LYA* | 2019 | 2020 | 2021 | LYA* | 2019 | 2020 | 2021 | |
January | 234.6 | 300.0 | 142.0 | 317.0 | 10.0 | 9.6 | 10.1 | 11.2 |
February | 152.1 | 127.0 | 97.0 | 26.0 | 10.7 | 11.4 | 11.1 | 12.3 |
March | 94.0 | 72.0 | 22.0 | 35.0 | 12.9 | 13.4 | 13.6 | 12.6 |
April | 49.4 | 149.0 | 27.0 | 4.0 | 16.4 | 15.8 | 16.6 | 16.8 |
May | 32.1 | 7.0 | 53.0 | 5.0 | 20.6 | 21.3 | 21.5 | 22.3 |
June | 11.0 | 13.0 | 1.0 | 18.0 | 25.3 | 25.8 | 23.8 | 25.0 |
July | 4.5 | 0.0 | 0.0 | 0.0 | 28.5 | 28.6 | 28.6 | 29.7 |
August | 4.5 | 0.0 | 1.0 | 1.0 | 28.4 | 28.7 | 28.4 | 28.3 |
September | 16.6 | 77.0 | 0.0 | 24.0 | 25.2 | 25.2 | 27.0 | 24.7 |
October | 67.9 | 19.0 | 26.0 | 14.0 | 20.6 | 22.5 | 22.0 | 20.6 |
November | 132.1 | 71.0 | 33.0 | 382.0 | 15.5 | 16.1 | 15.9 | 17.6 |
December | 261.2 | 262.0 | 440.0 | 236.0 | 11.6 | 11.8 | 13.3 | 13.3 |
Total | 1 060.0 | 1 097.0 | 842.0 | 1 062.0 | − | − | − | − |
Mean | − | − | − | − | 18.8 | 19.2 | 19.3 | 19.5 |
Long year average (1930–2021).
The soil was silty clay loam textured (19% sand, 31% clay and 50% silt) (Bouyoucos, 1951), with the following characterisations: pH of 8.0 (soil to water ratio 1:2.5); 24.7% CaCO3; 2.17% organic matter (Kacar, 2014), NaHCO3 extractable P 5 mg · kg−1 (Olsen and Sommer, 1982); 1N NH4OAC exchangeable K, Ca and Mg were 315, 4 763 mg · kg−1 and 402 mg · kg−1 respectively (Kacar, 2014). DTPA-extractable Fe, Cu, Zn and Mn concentrations (Lindsay and Norwell, 1978) were 7.99, 2.33, 0.50 and 6.86 mg · kg−1, respectively.
In the experiment chemical fertilizer (F), farmyard manure (FYM), vermicompost (VC), spent mushroom compost (SMC), chicken manure (CM) and control (C: non-fertilizer) were evaluated. The organic fertilizers were applied with the objective of obtaining 150 kg N · ha−1. As a result of the calculations performed on the basis of nitrogen concentrations and moisture contents of the organic fertilizers, 21 t · ha−1 FYM, 14 t · ha−1 SMC, 5 t · ha−1 CM and 13 t · ha−1 VC were applied. The analysis results of the organic materials used in the experiment are given in Table 2. FYM had the highest C content, and CM had the highest N concentration. The highest C/N belonged to FYM while the lowest C/N obtained with CM. Then, 325 kg · ha−1 urea (46% N), 200 kg · ha−1 potassium sulphate (50% K2O) and 200 kg · ha−1 triple superphosphate (44% P2O5) were applied to chemical fertilizer (F) application. The experiment was established on April 20, 2019, 1 month after the organic materials were applied to the soil, in a randomized complete block design (RCBD) with four replications.
The properties of organic fertilizers.
Parameters | FYM | SMC | CM | VC |
---|---|---|---|---|
pH | 8.8 | 7.4 | 8.2 | 9.1 |
EC (dS · m−1) | 1.11 | 5.11 | 5.98 | 2.65 |
Moisture (%) | 58 | 39 | 20 | 50 |
Dry matter (%) | 42 | 61 | 80 | 50 |
Organic matter (%) | 66 | 51 | 51 | 58 |
Ash (%) | 34 | 49 | 49 | 42 |
Total N (%) | 1.70 | 1.8 | 3.5 | 2.3 |
C (%) | 38 | 30 | 28.5 | 33.7 |
C/N | 22 | 17 | 8.14 | 14.6 |
Total P (%) | 0.36 | 0.40 | 2.03 | 0.65 |
Total K (%) | 1.45 | 2.30 | 3.45 | 2.60 |
Total Ca (%) | 7.0 | 7.7 | 12.55 | 3.97 |
Total Mg (%) | 0.98 | 1.51 | 1.03 | 1.05 |
Total Fe (mg · kg−1) | 2 380 | 5 075 | 1 625 | 7 500 |
Total Mn (mg · kg−1) | 288 | 393 | 394 | 350 |
Total Zn (mg · kg−1) | 90 | 185 | 414 | 140 |
Total Cu (mg · kg−1) | 29 | 53 | 62.5 | 40 |
Total Cd (mg · kg−1) | 2.9 | 2.4 | 2.0 | 2.85 |
Total Co (mg · kg−1) | 6.3 | 7.3 | 2.5 | 7.5 |
Total Cr (mg · kg−1) | 10.0 | 39.4 | 10.0 | 20.0 |
Total Ni (mg · kg−1) | 19.4 | 60.0 | 10.0 | 27.5 |
Total Pb (mg · kg−1) | 8.5 | 1.6 | 3.75 | 7.5 |
C, control; CM, chicken manure; F, NPK; FYM, farmyard manure; SMC, spent mushroom compost; VC, vermicompost.
Two harvests were carried out at the full flowering stage on 3 June, 2020 and 6 June, 2021. At the end of the first harvest, 150 kg N · ha−1, 90 kg P2O5 · ha−1 and 100 kg K2O · ha−1 were applied to the chemical fertilizer (F). Organic material applications were not repeated, and their effects in the following years were determined.
Harvests were done by sickle at a height of 5 cm above the soil surface. The fresh and dry herb yield (kg · ha−1) were determined by harvesting a 2.0 m2 area from each plot. The collected plants were dried in the shade until they reached a constant weight and were weighted by a digital balance.
Leaf samples were collected in a full flowering stage. Samples were dried at 40 °C in an oven for 2 days. Then, dry leaf samples of 20 g were suspended in 200 mL distilled water. Ground mass was subjected to hydrodistillation using Clevenger’s apparatus. After 3 h, the EOs were collected (Karık et al., 2018). Then, essential oil yield (EOY) was measured by using the following formula:
The EO composition of samples was analyssed by gas chromatography (Agilent 5975 C; Agilent Technologies, Santa Clara, CA, USA) coupled to a flame ionisation detector and mass spectrometry equipment (Agilent 5975 C) using a capillary column (HP Innowax Capillary; 60.0 m × 0.25 mm × 0.25 μm). EOs were diluted at 1:50 ratio with hexane. GC–MS/FID analysis was carried out at split mode of 50:1. Injection volume and temperature were adjusted as 1 μL and 250 °C, respectively. The relative percentage of components was calculated from GC-FID peak areas, and components were identified by Wiley 7n, Nist 05 and Flavor and Fragrance Natural, and Synthetic Compounds (ver.1.3) libraries.
Extraction of the samples was accomplished according to the method of Škerget et al. (2005) with some modifications. This extract was used: total phenolic and flavonoid contents with antioxidant activity using DPPH (2,2-diphenyl-1picrylhydrazyl). Total phenolic content (TPC) was analyzed by the Folin-Ciocalteu method (Škerget et al., 2005). Total flavonoid content (TFC) was determined by Chang et al. (2006). The antioxidant activity of the samples was analyzed by the DPPH assay according to the procedure of Maisuthisakul et al. (2007). The percent inhibition of the DPPH radical was calculated using the following equation: IP (%) = [(Ac – As)/Ac] × 100, where IP is the inhibition percentage and Ac and As are the absorbance values of the control and test sample, respectively. The extract concentration providing 50% inhibition [IC50 (milligrammes of dry weight (DW) of plant material per milligramme of DPPH)] was calculated by plotting the concentration versus IP (Dinçer et al., 2013).
The statistical analysis was made according to the principles set of Yurtsever (1984). All data were analysed using the JMP Statistical package programme developed by SAS (SAS Institute, Cary, NC, USA). Means were compared by analysis of variance (ANOVA), and the least significant difference (LSD) test at
The fresh herb yield of
The effects of applications on fresh and dry herb yield of oregano.
Treatments | Fresh herb yield (kg · ha−1) | Dry herb yield (kg · ha−1) | ||
---|---|---|---|---|
1st year | 2nd year | 1st year | 2nd year | |
C | 20 800 b | 24 060 c | 10 400 | 10 100 |
NPK | 25 320 a | 28 630 a | 12 910 | 11 660 |
FYM | 23 180 ab | 26 720 ab | 11 180 | 10 500 |
SMC | 21 980 b | 27 330 ab | 10 630 | 11 540 |
CM | 21 500 b | 25 410 bc | 10 890 | 10 480 |
VC | 21 660 b | 26 890 ab | 11 090 | 11 440 |
3.31* | 3.54* | 3.09ns | 2.63ns | |
LSD | 1 263 | 1 191 | − | − |
Significant at
C, control; CM, chicken manure; F, NPK; FYM, farmyard manure; SMC, spent mushroom compost; VC, vermicompost.
The effects of the applications on the EO content and yield of the oregano are shown in Figures 1 and 2. The EO content ranged from 3.61% to 5.42% in the first year of cultivation, the lowest EO was obtained with the control and the highest value was determined by CM. The applications increased the EO content in a range from 18.8% to 50.1%. In the second year of cultivation, EO content varied from 4.08% to 4.89% (
EOY ranged from 37.5 L · ha−1 to 59.1 L · ha−1 in the 1st year and 41.2 L · ha−1 to 52.6 L · ha−1 in the 2nd year. The EOY of oregano increased by 31.5%–57% with the direct effect of organic fertilizer, and the highest EOY was obtained by CM application. The residual effect of organic fertilizers increased EOY by 7.0%–27.6%, and the highest EOY was derived from VC and FYM. Bhaskar et al. (2001) noticed that the oil content of
Twenty-two constituents were identified in the EO of
Effects of applications on oregano EO components.
Components | C | F | FYM | SMC | CM | VC | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1st year | 2nd year | 1st year | 2nd year | 1st year | 2nd year | 1st year | 2nd year | 1st year | 2nd year | 1st year | 2nd year | 1st year | 2nd year | |
α-Pinene | 0.48 c | 0.54 | 0.57 ab | 0.56 | 0.61 a | 0.57 | 0.53 bc | 0.40 | 0.52 bc | 0.38 | 0.58 ab | 0.44 | 3.15* | 1.78ns |
α-Thujene | 1.21 b | 0.87 b | 1.37 ab | 1.29 a | 1.47 a | 0.98 b | 1.39 a | 0.88 b | 1.31 ab | 0.83 b | 1.47 a | 0.80 b | 2.91* | 4.32* |
Camphene | 0.25 | 0.35 bc | 0.26 | 0.38 bc | 0.30 | 0.54 ab | 0.29 | 0.60 a | 0.31 | 0.37 bc | 0.33 | 0.23 c | 1.30ns | 3.74* |
Myrcene | 1.45 b | 1.22 b | 1.58 b | 1.37 a | 1.90 a | 1.32 ab | 1.67 ab | 1.18 b | 1.57 b | 1.19 b | 1.65 ab | 1.27 ab | 2.98* | 3.15* |
α-Phellandrene | 0.26 ab | 0.23 | 0.23 b | 0.32 | 0.32 a | 0.23 | 0.21 b | 0.18 | 0.22 b | 0.17 | 0.20 b | 0.17 | 4.29* | 2.53ns |
β-Phellandrene | tr | 0.28 b | tr | 0.48 a | tr | 0.30 ab | tr | 0.18 b | tr | 0.16 b | tr | 0.23 b | − | 3.49* |
α-Terpinene | 1.73 | 1.16 | 1.67 | 1.24 | 1.94 | 1.18 | 1.81 | 1.18 | 1.72 | 1.39 | 1.88 | 1.28 | 0.61ns | 0.55ns |
Ɣ-Terpinene | 7.79 | 3.90 | 7.65 | 4.32 | 10.54 | 4.35 | 7.85 | 4.40 | 7.28 | 4.91 | 9.29 | 4.79 | 1.76ns | 0.76ns |
Limonene | tr | 0.40 b | tr | 0.37 bc | tr | 0.55 a | tr | 0.24 d | tr | 0.22 d | tr | 0.30 cd | − | 15.2*** |
1-Octen-3-ol | tr | 0.37 | tr | 0.53 | tr | 0.56 | tr | 0.41 | tr | 0.40 | tr | 0.37 | − | 4.16* |
p-Cymene | 7.97 | 4.19 b | 4.65 | 4.22 b | 5.85 | 4.20 b | 5.45 | 4.71 ab | 4.88 | 5.21 a | 4.92 | 4.54 b | 2.76ns | 3.64* |
trans-Sabinene hydrate | 0.50 | 0.55 | 0.23 | 0.65 | 0.35 | 0.63 | 0.38 | 0.52 | 0.39 | 0.61 | 0.47 | 0.44 | 1.40ns | 1.68ns |
Linalool | 0.31 | 0.17 c | 0.37 | 0.23 c | 0.56 | 0.68 b | 0.64 | 1.44 a | 0.24 | 0.25 bc | 0.32 | 1.17 a | 2.53ns | 13.14*** |
β-Caryophyllene | 3.83 a | 1.49 | 1.03 c | 1.97 | 2.26 b | 1.99 | 1.05 c | 1.86 | 0.86 c | 1.83 | 0.98 c | 1.83 | 36.7*** | 1.62ns |
α-Terpineol | 0.29 | 0.18 | 0.23 | 0.34 | 0.23 | 0.19 | 0.26 | 0.21 | 0.24 | 0.31 | 0.16 | 0.22 | 1.47ns | 2.36ns |
Terpinen-4-ol | 0.31 e | 1.78 | 1.28 c | 1.90 | 0.94 d | 1.45 | 2.19 a | 1.70 | 1.62 b | 2.10 | 1.13 cd | 1.78 | 32.4*** | 2.38ns |
Borneol | 1.29 | 0.67 c | 1.41 | 0.78 ab | 1.61 | 0.62 c | 1.57 | 0.82 a | 1.17 | 0.66 c | 1.51 | 0.69 bc | 1.27ns | 6.06** |
β-Bisabolene | 0.98 | 2.72 | 0.75 | 3.48 | 0.82 | 2.71 | 0.81 | 3.03 | 0.98 | 3.12 | 0.95 | 2.92 | 0.86ns | 0.99ns |
Germacrene D | 0.26 | 0.48 b | 0.32 | 0.49 b | 0.26 | 0.59 b | 0.34 | 0.57 b | 0.27 | 1.25 a | 0.27 | 0.55 b | 1.35ns | 34.3*** |
T-Cadinol | 0.40 | 0.87 bc | 0.21 | 1.20 a | 0.30 | 1.01 ab | 0.30 | 0.88 bc | 0.41 | 0.97abc | 0.24 | 0.68 c | 1.78ns | 2.95* |
Thymol | 13.87 ab | 19.27 | 7.35 bc | 12.20 | 6.77 c | 11.91 | 12.86 bc | 13.98 | 19.95 a | 16.51 | 12.43 bc | 16.04 | 4.77** | 1.62ns |
Carvacrol | 55.49 | 56.82 | 68.40 | 61.02 | 62.63 | 63.33 | 59.88 | 60.34 | 55.81 | 57.03 | 60.91 | 59.10 | 1.88ns | 0.95ns |
Means in the same row followed by the same letter are not significantly different at
Significant at
Significant at
Significant at
C, control; CM, chicken manure; F, NPK; FYM, farmyard manure; SMC, spent mushroom compost; VC, vermicompost.
Thymol was the second main constituent in the EO of
The
The effects of the applications on the TPC of the oregano were not significant (Figure 3). The TPC of oregano varied between 13.5 mg GAE · g−1 and 16.7 mg GAE · g−1 in the 1st year and 12.4 and 14.1 mg GAE · g−1 in the 2nd year. In the first year of cultivation, the lowest TFC of the oregano (4.8 mg · g−1) was determined by the control and the highest value (7.6 mg · g−1) by the VC (Figure 4). Compared with the TFC control, it increased by 25%–58% with organic fertilizers and by 48% with chemical fertilizers. The lowest TFC value (5.1 mg · g−1) was found in the control, and the highest value (10.5 mg · g−1) was determined by the residual effect of CM and VC in the 2nd year (
The DPPH radical scavenging activity of the plant was expressed by the IC50 value, which was defined as the concentration that inhibited the free radical by 50%. IC50 values varied between 12.7 mg DPPH · mL−1 and 20.4 mg DPPH · mL−1 in the first year and between 9.5 mg DPPH · mL−1 and 12.5 mg DPPH · mL−1 in the second year (Figure 5). VC stands out among the materials because a low IC50 value indicates high antioxidant activity due to high radical scavenging (Delgado et al., 2010). Yang et al. (2000) reported that organically grown cabbage, spinach and green pepper generally had higher levels of antioxidant activity.
The nitrogen (N), phosphorus (P), potassium (K) and calcium (Ca) concentrations of oregano varied from 1.85% to 1.97%, 0.18% to 0.22%, 1.92% to 2.13% and 1.21% to 1.34%, respectively, in 1st year. In the 2nd year, N, P, K and Ca concentrations of oregano varied from 1.96% to 2.11%, 0.20% to 0.23%, 2.12% to 2.29% and 1.23% to 1.38%, respectively (Table 5). The lowest values were determined by the control, and the highest concentrations were obtained by VC. Khomami (2011) reported that the highest N, P, K, Ca and Mg concentrations in
Effects of applications on macroelement concentration of oregano
Treatments | N (%) | P (%) | K (%) | Ca (%) | Mg (%) | |||||
---|---|---|---|---|---|---|---|---|---|---|
1st year | 2nd year | 1st year | 2nd year | 1st year | 2nd year | 1st year | 2nd year | 1st year | 2nd year | |
C | 1.85 b | 1.96 c | 0.18 c | 0.20 b | 1.92 c | 2.12 c | 1.21 c | 1.23 b | 0.20 | 0.22 |
F | 1.92 a | 2.08 ab | 0.19 bc | 0.22 a | 1.96 c | 2.27 ab | 1.33 ab | 1.30 ab | 0.22 | 0.25 |
FM | 1.92 a | 2.06 ab | 0.21 ab | 0.23 a | 2.06 b | 2.22 ab | 1.30 b | 1.28 b | 0.21 | 0.23 |
SMC | 1.95 a | 2.00 bc | 0.22 a | 0.22 a | 2.06 b | 2.21 b | 1.26 bc | 1.24 b | 0.22 | 0.23 |
CM | 1.93 a | 2.00 bc | 0.22 a | 0.22 a | 2.04 b | 2.20 bc | 1.26 bc | 1.27 b | 0.20 | 0.23 |
VC | 1.97 a | 2.11 a | 0.22 a | 0.22 a | 2.13 a | 2.29 a | 1.34 a | 1.38 a | 0.22 | 0.24 |
3.28* | 3.48* | 5.84** | 3.61* | 6.99** | 4.38** | 5.21** | 3.71* | 1.51ns | 1.26ns | |
LSD | 0.03 | 0.04 | 0.007 | 0.009 | 0.026 | 0.04 | 0.03 | 0.039 | − | − |
Means in the same row followed by the same letter are not significantly different at
Significant at
Significant at
C, control; CM, chicken manure ; F, NPK; FYM, farmyard manure; SMC, spent mushroom compost; VC, vermicompost.
The effects of applications on the microelement concentrations are given in Table 6. Fe concentration of oregano was changed between 256.25 mg · kg−1 and 280.27 mg · kg−1 in the 1st year. In the 2nd year, the lowest Fe (287.77 mg · kg−1) was taken from control, and the highest value (343.67 mg · kg−1) was obtained from FYM residual effect. Fe concentration of plant increased by 1.6%–19.4% with residual effects of organic fertilization as compared with the control. All of the applications caused an increase in Zn concentration. SMC gave the highest Zn with 21.00 mg · kg−1 and 19.76 mg · kg−1 in both years. Mn and Cu concentrations of oregano were increased by applications. Kocabaş et al. (2007) reported that the nutrient concentration of sage increased with organic manure applications.
Effects of applications on micro element concentration of oregano
Treatments | Fe (mg · kg−1) | Zn (mg · kg−1) | Mn (mg · kg−1) | Cu (mg · kg−1) | ||||
---|---|---|---|---|---|---|---|---|
1st year | 2nd year | 1st year | 2nd year | 1st year | 2nd year | 1st year | 2nd year | |
C | 256.25 | 287.77 d | 17.07 c | 16.16 c | 19.88 | 36.15 | 9.07 | 12.94 |
F | 257.75 | 328.52 ab | 17.37 c | 18.01 b | 22.12 | 44.31 | 9.74 | 13.09 |
FYM | 271.25 | 343.67 a | 18.45 bc | 18.78 ab | 20.38 | 36.55 | 9.60 | 13.13 |
SMC | 272.50 | 320.80 abc | 21.00 a | 19.76 a | 25.71 | 37.90 | 10.04 | 13.04 |
CM | 260.27 | 297.02 bcd | 20.17 ab | 17.62 b | 21.28 | 39.06 | 10.68 | 13.06 |
VC | 280.27 | 292.32 cd | 18.50 bc | 18.22 b | 21.32 | 39.85 | 9.57 | 13.13 |
0.49ns | 4.30** | 5.09** | 6.46** | 1.54ns | 1.48ns | 0.79ns | 0.20ns | |
LSD | − | 15.40 | 0.97 | 0.67 | − | − | − | − |
Means in the same row followed by the same letter are not significantly different at
Significant at
Significant at
C, control; CM, chicken manure; F, NPK; FYM, farmyard manure; SMC, spent mushroom compost; VC, vermicompost.
Chemical and organic fertilizers applied led to remarkable improvement in biomass of oregano. The highest herb yield was obtained with chemical fertilizers and FYM. The highest EO contents were obtained from SMC and FYM according to years. VC was the most effective application for the antioxidant activity and nutrient status of oregano in both years. As a result of this research, organic fertilizers can be used to achieve yield, EO contents and nutrient uptake of oregano.