Soybean (
Over the past decades, some of SCN hatching factors have been identified, e.g., glycinoeclipines A, B, and C isolated from aqueous root extracts of bean (
Nonetheless, the studies that sought to identify SCN hatching factors concentrated on compounds from root extracts or exudates (Fukusawa et al., 1985; Masamune et al., 1987; Riga et al., 2001) without investigating the role of short-chain molecules, such as the volatile organic compounds (VOCs). Although studies on the effects of VOCs on hatching are scarce, the nematicidal activity of these molecules have received more attention (Aissani et al., 2015; Barros et al., 2014; Silva et al., 2018, 2019). In addition, many of them have the potential to be used as soil biofumigants (Gomes et al., 2020; Ntalli et al., 2018; Pedroso et al., 2019).
Soybean, bean, ryegrass, and alfalfa plants have exudates and root extracts that stimulate the hatching of the SCN (Riga et al., 2001). In this paper, we investigated the role of VOCs released by these plants as
The isolate of
Six replicates of treatments were prepared similar to the ones described in the previous item for the characterization of volatile compounds. The samples were added in 20 ml solid phase microextraction (SPME) flasks and kept closed for five days in an incubator at 25°C. The identification of volatile molecules was carried at the Center for Analysis and Chemical Prospecting (Department of Chemistry/UFLA). VOCs were extracted via headspace solid phase microextraction (SPME) (Arthur and Pawliszyn, 1990). The parameters for SPME and gas chromatography-mass spectrometry (GC-MS) were identical to those described in previous work by Gomes et al. (2020).
The effect of four VOCs identified on the gaseous emissions of plants leaves and roots was evaluated on the hatching of
The VOCs that caused hatching inhibition in the previous trial were selected to assess their toxicity to the J2. For this purpose, was determined the lethal concentration values required to kill 50% of the nematode population (LC50) of the compounds 1-hexanol and 3-octanol. The compounds were prepared similarly to that described in the previous item; however, the final concentrations were adjusted to 10, 50, 100, 150, 200, 250, and 300 µg/ml. Then, 0.5 ml of the aqueous solution of each compound plus 0.5 ml of the J2 suspension (300 J2) were placed in 2 ml micro tubes. The micro tubes were sealed with plastic PVC film and incubated at 25°C for 48 hr. After this period, the micro tubes were opened and an aliquot of 100 µl of each replicate was added in holes of 96-well polystyrene plates to determine J2 mortality. The determination of dead nematodes was performed by adding 20 µl of 1 mol/l sodium hydroxide solution (NaOH) to each hole in the plate (Chen and Dickson, 2000). Nematodes that remained immobile after 3 min were considered dead. The J2 mortality percentages obtained in each treatment were used to calculate the LC50 of each of the compounds, which represents the concentration capable of killing 50% of the J2 population of
The experiments were carried out twice in completely randomized designs with five replicates per treatment in hatching tests, and with six replicates for the lethal concentration experiment. Combined analysis of the experiments (Experiment 1× Experiment 2) was performed and in all tests, it was significant (
In two experiments, the VOCs emitted by the different plant species induced a significant increase (
Percentage of
Hatching (%) | ||||
---|---|---|---|---|
Treatment | Experiment 1 | SDZ | Experiment 2 | SDZ |
Controlx | 12.6yc | 1.58 | 14.0d | 1.23 |
Alfalfa leaves | 18.7b | 3.17 | 17.5b | 0.82 |
Ryegrass roots | 18.8b | 2.95 | 15.7c | 0.76 |
Bean roots | 19.8a | 2.01 | 18.1b | 1.61 |
Bean leaves | 20.6a | 1.71 | 16.4c | 0.77 |
Soybean roots | 21.3a | 2.49 | 20.0a | 1.24 |
Soybean leaves | 21.6a | 1.60 | 18.6b | 2.00 |
GC-MS analysis of the VOCs released by the roots of soybean, ryegrass, and bean revealed the presence of 22, 19, and 17 compounds, respectively. In the emissions of soybean, bean, and alfalfa leaves, 14, 5, and 7 compounds were found, respectively. More compounds were found in soybean and bean roots emissions than in leaves (Table 2). In general, most of the compounds found belong to the classes of alcohols, esters, and ketones, but with incidence of some compounds in the furans, aldehydes, terpenes, pyrazines, and other classes. The compounds 1-hexanol and 2-octanone were detected in all analyzed root emissions (ryegrass, soybean, and bean), but were not identified in the leaf samples. The compounds 2-octanol, 3-methyl-1-butanol, 2-methyl-1-butanol, 6-methyl-5-heptan-2-ol, 2-ethyl-1-hexanol, 2-octanone, 3-octanone, 6-octen-2-one, pentan-3-one, and ethylene benzene were detected only in soybean and bean roots. Some compounds were identified exclusively in certain plant material, such as: heptyl acetate, octyl acetate, isopulegol acetate, n-nonyl acetate, p-ethylanisole, and 4-ethyl-1,2-dimethoxybenzene in ryegrass roots; 3-octanol, lavandulol, 2-butanone, ionone and linalool in soybean leaves; hexanal, b-felandrene, 2-isopropyl-3-methoxypyrazine and 2-sec-butyl-3-methoxypyrazine in soybean roots; and, 1-octen-3-ol, ethyl 2-methylbutyrate, and ethyl butyrate on alfalfa leaves. Three compounds were not identified including two sesquiterpenes. All compounds detected showed low intensity peaks in the samples and, therefore, were categorized only as minor peaks (+).
Volatile organic compounds from leaves or roots of soybeans, beans, ryegrass, and alfalfa characterized by GC-MS.
Compound | RI exp.a | RI lit.b | Ryegrass roots | Soybean leaves | Soybean roots | Bean leaves | Bean roots | Alfalfa leaves |
---|---|---|---|---|---|---|---|---|
|
||||||||
Ethanol | + | + | + | + | ||||
3-Octanol | 1,001 | 993 | + | |||||
2-Octanol | 1,005 | 997 | + | + | ||||
3-Methyl-1-butanol | 737 | 734 | + | + | + | + | + | |
2-Methyl-1-butanol | 745 | 738 | + | + | + | + | ||
1-Hexanol | 872 | 867 | + | + | + | |||
1-Octen-3-ol | 984 | 978 | + | |||||
6-Methyl-5-hepten-2-ol | 1,000 | 992 | + | + | + | |||
2-Ethyl-1-hexanol | 1,032 | 1,029 | + | + | + | |||
|
||||||||
Ethyl 2-methylbutyrate | 845 | 848 | + | |||||
Ethyl butyrate | 801 | 802 | + | |||||
Ethyl acetate | 627 | 623 | + | + | ||||
Hexyl acetate | 1,014 | 1,014 | + | + | ||||
Decyl acetate | 1,409 | 1,408 | + | |||||
Heptyl acetate | 1,113 | 1,113 | + | |||||
Octyl acetate | 1,211 | 1,211 | + | |||||
n-Nonyl acetate | 1,310 | 1,302 | + | |||||
|
||||||||
2-Ethylfuran | 705 | 708 | + | + | ||||
2-Pentylfuran | 990 | 991 | + | + | + | |||
|
||||||||
2-Butanone | 605 | 605 | + | |||||
2-Pentanone | 703 | 695 | + | + | ||||
2-Octanone | 991 | 990 | + | + | + | |||
3-Octanone | 988 | 986 | + | + | + | + | ||
6-Octen-2-one | 985 | 985 | + | + | ||||
3-Pentanone | 704 | 700 | + | + | + | |||
2-Nonanone | 1,092 | 1,091 | + | + | ||||
3,5-Octadien-2-one | 1,072 | 1,068 | + | + | ||||
|
||||||||
Hexanal | 806 | 800 | + | |||||
|
||||||||
Linalool | 1,103 | 1,007 | + | |||||
M-Cymene | 1,024 | 1,023 | + | + | + | + | ||
B-phellandrene | 1,030 | 1,025 | + | |||||
Lavandulol | 1,167 | 1,165 | + | |||||
Isopulegol acetate | 1,271 | 1,273 | + | |||||
Sesquiterpene* | 1,426 | + | ||||||
Sesquiterpene* | 1,432 | + | ||||||
Ionone | 1,482 | 1,485 | + | |||||
|
||||||||
3-Methoxy-2,5-dimethyl | 1,051 | 1,057 | + | + | ||||
pyrazine | ||||||||
2-Isopropyl-3-methoxy | 1,089 | 1,093 | + | |||||
pyrazine | ||||||||
2-Sec-butyl-3-methoxy | 1,167 | 1,164 | + | |||||
pyrazine | ||||||||
|
||||||||
P-Ethylanisole | 1,114 | 1,104 | + | |||||
Ethenyl-benzene | 895 | 891 | + | + | + | + | ||
4-ethyl-1,2-dimethoxy | 1,322 | + | ||||||
benzene | ||||||||
Unidentified | 1,019 | + | + |
In two experiments, none of the compounds tested at concentrations of 200, 600, and 1000 µg/ml, namely 3-octanol, 1-hexanol, hexanal and linalool, induced J2 hatching at the same level as the positive control (ZnCl2). Furthermore, the solubilizing agent used to dissolve the compounds – 1% Tween 80 – when tested alone was more effective in inducing hatching than the solutions containing the compounds. In the second experiment, the solubilizing agent Tween 80 at 1% showed similar hatching percentage (
If, on the one hand, none of the compounds acted as hatching factors, the compounds 3-octanol and 1-hexanol caused, in the three concentrations tested in both assays, a reduction in hatching (
Percentage of
Hatching (%) | |||
---|---|---|---|
Treatment | Concentration (µg/mlor mMx) | Experiment 1 | Experiment 2 |
Water | – | 15.2yd | 30.2b |
Carbofuran | 415 | 3.0f | 4.6c |
Zinc chloride | 3x | 31.4a | 44.4a |
Tween 80 | – | 27.3b | 44.6a |
Hexanal | 1,000 | 25.3c | 31.0b |
600 | 23.8c | 28.0b | |
200 | 22.7c | 30.1b | |
Linalool | 1,000 | 13.3d | 26.0b |
600 | 15.3d | 25.0b | |
200 | 16.8d | 28.4b | |
1-Hexanol | 1,000 | 2.9f | 5.3c |
600 | 1.9f | 4.1c | |
200 | 3.4f | 5.5c | |
3-Octanol | 1,000 | 3.8f | 5.0c |
600 | 3.3f | 8.3c | |
200 | 7.5e | 8.8c |
In two assays, the increase of 1-hexanol and 3-octanol concentrations caused increase in
The hatching induction of
In this work, the identification of VOCs released by plants though GC-MS allowed the investigation of the interaction of some VOCs with the SCN. Four molecules, 3-octanol, 1-hexanol, hexanal and linalool were selected for more in-depth tests of hatching stimulus. While, none of them acted as hatching inducer, two of them 3-octanol and 1-hexanol caused hatching inhibition. We should emphasizing that this result occurred from the three concentrations test. Therefore, the possible action of these molecules as SCN hatching inducer when in different concentrations cannot be excluded. In addition, the synergistic effect between the compounds was also not evaluated. Indeed, our results strongly suggest that a synergistic mechanism is in place and that a more complex mixture of the compounds is needed to trigger the SCN hatching than just one single compound. The synergistic effect of different compounds on the hatching of cyst nematodes has been reported in the literature. Potato root leachate contain multiple hatching factors that exhibit a synergistic effect with one another, as seen in purified isolates stimulating lower hatch compared to the crude (Devine and Jones, 2000b). Thus, from the catalog of molecules presented here, further research can be carried out seeking to identify an individual molecule or a mixture of compounds that have the characteristic of SCN hatching factor.
In recent years, studies have revealed VOCs emitted by plant residues with nematicidal activity similar to commercial nematicides (Gomes et al., 2020; Silva et al., 2018). In the present study, several compounds identified in plant emissions, such as 3-methyl-1-butanol, 2-methyl-1-butanol, 3-pentanone, 2-nonanone, linalool, m-cymene, 2-octanol, 2-ethyl-1-hexanol, ethyl acetate, 2-ethylfuran and 2-octanone have proven nematicidal activity (Aissani et al., 2015; Gu et al., 2007; Hewavitharana et al., 2014; Sharma et al., 2018; Zhai et al., 2018). In this sense, the compounds 3-octanol detected in soybean leaves and 1-hexanol detected in soybean, bean, and ryegrass roots, were toxic to eggs and
Interestingly, Tween 80 (negative control) used for dissolving VOCs stimulated hatching at a value similar to ZnCl2 (positive control). The change in eggshell permeability may be a central point in the hatching of cyst nematodes (Perry and Trett, 1986). In studies with lepidopterans such as
Having a more comprehensive knowledge of the chemical constituents of plant diffusates will lead to our better understanding of the interactions between
Raw data related to Table 1.
Treatments | Time | Total_J2_hatched | %_J2_hatched |
---|---|---|---|
Control | 1 | 147 | 13.01 |
Control | 1 | 125 | 11.06 |
Control | 1 | 169 | 14.96 |
Control | 1 | 127 | 11.24 |
Control | 1 | 145 | 12.83 |
Control | 2 | 159 | 13.25 |
Control | 2 | 183 | 15.25 |
Control | 2 | 177 | 14.75 |
Control | 2 | 147 | 12.25 |
Control | 2 | 175 | 14.58 |
Soybean roots | 1 | 277 | 24.51 |
Soybean roots | 1 | 224 | 19.82 |
Soybean roots | 1 | 203 | 17.96 |
Soybean roots | 1 | 250 | 22.12 |
Soybean roots | 1 | 249 | 22.04 |
Soybean roots | 2 | 218 | 18.17 |
Soybean roots | 2 | 258 | 21.50 |
Soybean roots | 2 | 235 | 19.58 |
Soybean roots | 2 | 244 | 20.33 |
Soybean roots | 2 | 245 | 20.42 |
Bean roots | 1 | 218 | 19.29 |
Bean roots | 1 | 219 | 19.38 |
Bean roots | 1 | 227 | 20.09 |
Bean roots | 1 | 258 | 22.83 |
Bean roots | 1 | 195 | 17.26 |
Bean roots | 2 | 185 | 15.42 |
Bean roots | 2 | 234 | 19.50 |
Bean roots | 2 | 220 | 18.33 |
Bean roots | 2 | 230 | 19.17 |
Bean roots | 2 | 219 | 18.25 |
Ryegrass roots | 1 | 209 | 18.50 |
Ryegrass roots | 1 | 169 | 14.96 |
Ryegrass roots | 1 | 234 | 20.71 |
Ryegrass roots | 1 | 254 | 22.48 |
Ryegrass roots | 1 | 194 | 17.17 |
Ryegrass roots | 2 | 200 | 16.67 |
Ryegrass roots | 2 | 189 | 15.75 |
Ryegrass roots | 2 | 186 | 15.50 |
Ryegrass roots | 2 | 175 | 14.58 |
Ryegrass roots | 2 | 192 | 16.00 |
Soybean leaves | 1 | 236 | 20.88 |
Soybean leaves | 1 | 224 | 19.82 |
Soybean leaves | 1 | 273 | 24.16 |
Soybean leaves | 1 | 243 | 21.50 |
Soybean leaves | 1 | 242 | 21.42 |
Soybean leaves | 2 | 261 | 21.75 |
Soybean leaves | 2 | 195 | 16.25 |
Soybean leaves | 2 | 223 | 18.58 |
Soybean leaves | 2 | 215 | 17.92 |
Soybean leaves | 2 | 220 | 18.33 |
Bean leaves | 1 | 215 | 19.03 |
Bean leaves | 1 | 217 | 19.20 |
Bean leaves | 1 | 250 | 22.12 |
Bean leaves | 1 | 256 | 22.65 |
Bean leaves | 1 | 223 | 19.73 |
Bean leaves | 2 | 198 | 16.50 |
Bean leaves | 2 | 197 | 16.42 |
Bean leaves | 2 | 192 | 16.00 |
Bean leaves | 2 | 186 | 15.50 |
Bean leaves | 2 | 211 | 17.58 |
Alfalfa leaves | 1 | 184 | 16.28 |
Alfalfa leaves | 1 | 172 | 15.22 |
Alfalfa leaves | 1 | 203 | 17.96 |
Alfalfa leaves | 1 | 251 | 22.21 |
Alfalfa leaves | 1 | 246 | 21.77 |
Alfalfa leaves | 2 | 217 | 18.08 |
Alfalfa leaves | 2 | 209 | 17.42 |
Alfalfa leaves | 2 | 216 | 18.00 |
Alfalfa leaves | 2 | 214 | 17.83 |
Alfalfa leaves | 2 | 193 | 16.08 |