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Original article
01 2021
:15;
103482
doi:
10.1016/j.arabjc.2021.103482

Pesticidal potential of some wild plant essential oils against grain pests Tribolium castaneum (Herbst, 1797) and Aspergillus flavus (Link, 1809)

Department of Chemistry, COMSATS University Islamabad, Abbottabad Campus, Abbottabad 22060, Pakistan
Department of Environmental Sciences, COMSATS University Islamabad, Abbottabad Campus, Abbottabad 22060, Pakistan
Department of Plant Pathology, Faculty of Agricultural Sciences and Technology, Bahauddin Zakariya University, 60800 Multan, Pakistan
Laboratory of Chemical and Behavioural Ecology, Institute of Ecology, Nature Research Centre, Akademijos str. 2, LT-08412 Vilnius, Lithuania
Department of Zoology, Stockholm University, Svente Arrhenius vag 18B, SE, Stockholm, Sweden
Department of Botany and Microbiology, College of Science, King Saud University, Riyadh 11451, Saudi Arabia

⁎Corresponding authors. muhazeem@cuiatd.edu.pk (Muhammad Azeem), amabbasi@cuiatd.edu.pk (Arshad Mehmood Abbasi),

Disclaimer:
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

Abstract

  • Essential oils of wild plant, Conyza sumatrensis exhibited excellent insecticidal activity against red flour beetle, Tribolium castaneum.

  • Erigeron canadensis and Chenopodium ambrosioides inhibited the growth of Aspergillus flavus.

  • The major component of C. sumatrensis essential oil was cis-lachnophyllum ester.

  • Major components of Erigeron canadensis and Chenopodium ambrosioides were limonene and α-terpinene respectively.

Abstract

The red flour beetle, Tribolium castaneum, and the mold Aspergillus flavus are well known threats of stored grain commodities, causing nutritional loss and poisoning of stored products, respectively. T. castaneum has developed resistance against most insecticides, leading to the use of extensive amounts of synthetic insecticides to protect stored grains. Synthetic pesticides not only toxify the environment but also cause serious health issues in humans using pesticide treated grains. This study aimed to identify plant-based natural pesticides to control T. castaneum and A. flavus. Essential oils were extracted from fresh aerial parts of Chenopodium ambrosioides, Conyza sumatrensis, Erigeron canadensis, and Tagetes minuta through steam distillation and investigated for insecticidal and anti-fungal activities against adult T. castaneum and A. flavus, respectively. GC–MS analysis of C. sumatrensis revealed the presence of 37.7% cis-lachnophyllum ester, 13.4% germacrene D, and 21.6% limonene, whereas in E. canadensis the major compounds were limonene, germacrene D, and cis-lachnophyllum ester (43.4%, 12.9% and 5.9%, respectively). In bioassays with treated grain, C. sumatrensis and E. canadensis essential oils exhibited excellent toxicity against adult T. castaneum with LD50 of 3.7 and 5.6 mg per 10 g grains whereas in a fumigation bioassay they showed LD50 of 6.6 and 10.6 mg/L, respectively. The essential oils extracted from C. ambrosioides and E. canadensis exhibited good anti-fungal activity against A. flavus. Our findings suggest that essential oils of C. sumatrensis and E. canadensis can play an important role in protecting stored grains from T. castaneum and A. flavus contamination.

Keywords

Tribolium
Aspergillus
Stored grain
Essential oil
Pest control
1

1 Introduction

The world population is increasing at a fast pace and it is estimated to reach 10 billion by 2050 (FAO, 2017; Zaka et al., 2019). Due to this growing population, the consumption of food commodities is also increasing, leading to food security issues in large parts of the world, but especially in developing and under-developed world. The availability of food is an important pillar in food security that not only depends upon the production of food commodities, but also on their maintenance and protection from post-harvest insect pests and pathogens (FAO, 2017).

Insect pests cause serious damage to grains and their products worldwide. It is estimated that about 10% of annually produced grains and their products are destroyed during post-harvest storage due to pest activities (Sallam, 1999). The post-harvest loss of grains is even worse in developing and under-developed countries situated in the world’s warm climate regions, where losses exceeds 25% (Manandhar et al., 2018). In major part of Asia and Africa, small farmers grow grain crops to fulfil their families’ and local communities’ food requirements. It is a common practice of small farmers and merchandisers to store grains to be used as seeds or to sell later at better prices. Due to the lack of facilities for proper storage, large parts of stored grains are destroyed because of fungal or insect infestations (Manandhar et al., 2018). In Pakistan, the post-harvest storage loss was estimated to be 16% of production, or 3.2 million tons annually (Fox & Fimeche, 2013). Among stored-product pests, beetles cause the highest losses (Culliney, 2014).

The red flour beetle, Tribolium castaneum (Herbst, 1797) (Coleoptera: Tenebrionidae) is one of the most common and damaging pests of stored grain products and is considered a model species for studies of post-harvest pest control (Brown et al., 2009). This serious insect pest is distributed worldwide and damages stored products in most warehouses of tropical and sub-tropical regions (Pimentel et al., 2007). Adults of T. castaneum prefer to feed on the endosperm part of the seed, while larvae target the germ. Usually, the insect pests that prefer feeding on the germ of seeds are the most damaging (Dal Bello et al., 2001).

Stored-grain insect pests are mainly controlled by using organophosphate and pyrethroid insecticides (Sousa et al., 2008). Apart from insecticides, fumigants such as methyl bromide, aluminum phosphide, and magnesium phosphide are extensively used to protect stored grains from insect pests (Olivero-Verbel et al., 2010). The use of synthetic insecticides not only adversely affects the environment, but also causes toxicity to human food chains (Caballero-Gallardo et al., 2011; Dal Bello et al., 2001; Huang et al., 1997).

Methyl bromide is an widely used fumigant for the control of stored-grain pests, but according to World Meteorological Organization (WMO) reports, methyl bromide causes ozone depletion and harms warm-blooded animals, including humans (Lee et al., 2001a). Phosphine is another fumigant that is often used to protect stored grain against insect pests, however, a decreasing trend of phosphine fumigation has been observed because many insect pests have gained resistance against it (Pimentel et al., 2007; Suthisut et al., 2011). Moreover, it possesses genotoxicity to occupationally exposed fumigators (Lee et al., 2001b).

Aspergillus flavus (Link, 1809) (Eurotiales: Trichocomaceae) is one the most harmful post-harvest pathogenic fungi of food crops and nuts throughout the world (Klich, 2007). The infection of this fungus not only decreases grain quality but also compromises its palatability. A. flavus produces aflatoxins which are toxic to mammals (Agrios, 2005), highly carcinogenic, and are considered 1A carcinogens by the International Agency for Research on Cancer (IARC) (Ostry et al., 2017).

Since early human civilization, plant-based substances have been utilized as drugs, pharmaceuticals, perfumery products, cosmetics, aroma compounds, insect repellents, insecticides, and antibiotics, etc. A number of studies reported the importance of plant-based products to be used for the control of insect pests (Ahmad et al., 2019; Khan et al., 2017; Zaka et al., 2019), as insect repellents (El-Seedi et al., 2017; Jaenson et al., 2006), and insecticides (Cardiet et al. 2012; Kim & Park, 2008). A number of previous studies described the screening of insecticidal activity of plant essential oils (Ebadollahi et al. 2020) or extracts, but most of them did not report the chemistry of essential oils or extracts (Shahzadi et al. 2010; Zaka et al. 2019). In this study, we investigated the insecticidal and anti-fungal potential of the essential oils of four wild plants against two economically important pests of stored products, T. castaneum and A. flavus. Essential oils were extracted from Chenopodium ambrosioides, Conyza sumatrensis, Erigeron canadensis, and Tagetes minuta, and their chemical composition determined using GC–MS for possible correlation between bioactivity and chemistry of essential oils. The LD50 and LD90 values were also calculated to find essential oils with potent activity.

2

2 Material and methods

2.1

2.1 Plant material

Fresh aerial parts of Chenopodium ambrosioides L., Conyza sumatrensis (Retz.) Erigeron canadensis L. and Tagetes minuta L. were collected from two different areas of Abbottabad, Pakistan (Table 1). The plant samples were identified by Dr. Abdul Nazir and voucher specimens were submitted to the herbarium of the Environmental Sciences Department, COMSATS University Islamabad, Abbottabad Campus, Abbottabad, Pakistan. Plant material was maintained at −20 °C until essential oil extraction.

Table 1 Percentage yield of essential oils extracted from fresh aerial parts of plants.
Voucher # Plant name Family Collection month Coordinates Yield of essential oils (%)
CUHA-207 Chenopodium ambrosioides L. Chenopodiaceae June 34°10′52.3″ N, 73°14′05.8 “E 0.11
CUHA-208 Conyza sumatrensis Retz. Asteraceae 34°10′52.3″ N, 73°14′05.8 “E 0.25
CUHA-209 Erigeron Canadensis L. Asteraceae 34°10′52.3″ N, 73°14′05.8 “E 0.31
CUHA-101 Tagetes minuta L. Asteraceae November 34°12′34.5″ N, 73°19′49.0″ E 0.61

2.2

2.2 Essential oil extraction

Steam distillation was used to extract essential oils from the plant material, as described earlier (Azeem et al., 2019). Briefly, fresh aerial parts were chopped with a knife and 1,500 g was subjected to steam distillation in a stainless-steel distillation apparatus. Distilled water was added to the distillation vessel that did not have direct contact with the plant material which was packed in a meshed container fitted in the vessel above water level. The vessel was heated on an electrical heating mantle and the distillate containing the plant’s volatile compounds, along with condensed steam, was collected in a separating funnel for 4 h. The layer of essential oil at the top of the water was separated through decantation. The remaining distillate was further used to collect essential oil through liquid–liquid extraction (LLE) by using HPLC grade n-hexane. A small amount of anhydrous magnesium sulphate was added to the n-hexane extract for the complete elimination of water. After filtration, the n-hexane was evaporated under vacuum in a rotary evaporator. The essential oil isolated through decantation and LLE were combined and weighed to determine the percent yield. Purified samples were stored at −20 °C until insecticidal and anti-fungal experiments and chemical analysis.

2.3

2.3 Chemical profiling of essential oils

The chemical composition of the essential oils was determined by a Hewlett Packard 6890 N gas-chromatograph (GC) coupled with a HP 5973 mass spectrometer (MS, Agilent Technologies Inc. USA). The GC was equipped with a DB-5 column (30 m length, 0.25 mm internal diameter and 0.25 µm stationary phase film thicknesses). The injector was operated at 235 °C and the oven temperature was programmed as follows: isothermally at 40 °C for 2 min, then increased by 4 °C per min to 240 °C, and afterwards held isothermally at 240 °C for 8 min. The carrier gas was high purity Helium (99.99%) with a constant flow of 1 mL/min. Injections of 1 µL essential oil solutions (1 mg/mL) were made in splitless mode for 30 sec. Mass spectral detection was performed by an electron ionization system operated at the ionization energy of 70 eV. The ion source temperature of MS was set at 180 °C and the solvent delay for an injection was set for 5 min. The mass spectra of separated compounds were scanned from 30 to 400 amu.

GC peak areas were used to determine the percentage composition of essential oils without using correction factors. The identification of the essential oils’ constituents were initially carried out by comparing their mass spectra and retention indices with those available in National Institute of Standards and Technology (NIST) 2008 MS library and from the literature (Adams, 2007). In order to calculate retention indices of essential oil constituents, a standard solution of straight chain alkanes (C9-C24) was injected in the GC–MS using the same parameters used for essential oil analysis. Finally, wherever possible, the identification of compounds was achieved by injecting solutions of authentic pure standards.

2.4

2.4 Insect rearing

Red flour beetles were maintained in the laboratory following a reported procedure (Bouda et al., 2001; Dal Bello et al., 2001). Briefly, T. castaneum adults were collected from infested rice purchased from a local market in Abbottabad. Adult beetles were provided insecticide-free wheat flour and maintained in plastic jars (18 × 10 × 10 cm) in an incubator at 25 ± 3 °C and 60 ± 10 % relative humidity (RH) with alternating light–dark cycles of 12 h. A cheese cloth was used to close the jar mouths. The adults obtained from the infested rice were transferred to another jar by sieving after two weeks. Once new adult beetles started emerging, they were transferred to separate jars. The jars with eggs and larvae were observed regularly to separate newly emerged T. castaneum adults in fresh jars containing flour. The process was continued until sufficient numbers of beetles were obtained for experiments.

2.5

2.5 Insecticidal bioassay through treated grains

The insecticidal activity of essential oils was tested through food poisoning method by adopting methods described by Bouda et al. (2001) and Hematpoor et al. (2017) with some modification. Essential oil (40 mg) was dissolved in 1 mL of ethanol and the resulting solution was applied on 10 g of rice and shaken well for 15 min by using a rotary shaker (Hashem et al. 2018). Thus, the concentration of essential oil on rice was 0.4% (w/w). For a control treatment, the same amount of rice were treated with 1 mL of ethanol. Both control and essential oil treated rice samples were dried at room temperature for 20 min prior to use in bioassays. The control and essential oil treated rice samples were placed at the center of two separate 90 mm glass Petri plates and fifteen unsexed adults T. castaneum (4–7 day old and 24 h starved) were released in each Petri plate. The Petri plates were covered with lids and incubated at 25 ± 3 °C and 60 ± 10 % RH with alternating light–dark cycles of 12 h. The numbers of live beetles in each Petri plate were counted after 24 h, 48 h, and 72 h exposure, followed by 24 h recovery time. A beetle was considered alive if it moved its legs or antenna upon prodding with a soft forceps. Five replicates of each essential oil or control were run in similar way and the experiment was carried out in duplicate. Chlorpyrifos solution was used as positive control. To find the lethal dose, the experiments were run using decreasing doses, such as 20 mg, 10 mg, 5 mg and 2.5 mg, and same number of replicates and experiments were employed for all doses tested.

2.6

2.6 Insecticidal bioassay through fumigation

The fumigant bioassay was carried out by using a published method (Khani & Rahdari, 2012; Negahban et al., 2007; Sriti Eljazi et al., 2017) with some modifications. Various concentrations of essential oils were prepared in ethanol, thus the fumigant concentration in gas tight jars were 2.5 mg/L to 40 mg/L (2.5 ppm − 40 ppm) by using a two-fold dilution in each step. One side of a filter paper strip (2 cm width and 6 cm length) was impregnated with 10 µL of essential oil solution. After drying for 5 min at room temperature, the untreated side of the filter paper strip was attached to the internal side of the jar lid and the gas-tight lid was placed on each of the glass jars each of 100 mL volume. The sample-bearing side of the filter paper strip was suspended inside the glass jar at the height of 2 cm from the bottom of the jar. This fumigation setup was made to prevent direct contact of the insects with the test substance or control. In each glass jar, fifteen unsexed adult beetles were released. They were 7–12 days old and starved for 24 h. The beetles were exposed to the vapors of the test essential oil or negative control (ethanol) or chlorpyrifos and the dead beetles were counted after 72 h of exposure time. In order to check the mortality of the beetles, they were removed from the testing jar and the insects showing no movement of legs upon piercing with a tweezer were considered dead. The fumigation bioassays were repeated twice using five replicates in each experiment. Total numbers of surviving insects in the control and test substance jar were counted and percent insect mortality was calculated by using the following formula:

% Mortality = [Numbers of live beetles in control treatment - Numbers of live beetles in test treatment] × 100/ [Numbers of live beetles in control treatment].

2.7

2.7 Anti-fungal bioassay

A strain of Aspergillus flavus was isolated from the contaminated food commodity by inoculating it on potato dextrose agar (PDA) at 28 ± 1 °C for 72 h. The isolated fungal colony was inoculated on fresh PDA Petri plates until a purified single colony was obtained. The fungal strain was identified based on morphological characteristics and maintained on PDA and stored at 4 °C until being used for anti-fungal bioassays. To determine anti-fungal activity of extracted essential oils, an earlier reported agar well diffusion method was used (Mekonnen et al., 2016). Briefly, sterilized molten PDA medium was poured into 90 mm sterilized Petri plates and left to solidify overnight on a clean bench. Fungal inoculum was prepared by making the fungal spore suspension in sterilized distilled water from the pure culture plate and then used for the experiment. An aliquot of 100 μL fungal inoculum containing 105 conidia/mL was spread evenly on the PDA Petri plate with the help of glass spreader and the plate was incubated for 30 min so that the inoculum would be completely absorbed on the medium surface. One well of 6 mm diameter was dug in the center of the PDA Petri plate with the help of a sterilized cork-borer. Essential oil (10 μL) was added into the well whereas on the control Petri plate 10 µL dimethyl sulfoxide (DMSO) was added. Dithane M45 solution was used as positive control. All the plates were incubated in a laminar flow hood for 30 min, so that the essential oil and control samples could diffuse into the agar. The Petri plates were incubated at 28 ± 2 °C for 72 h. After the incubation period, the inhibition zone around the well was measured in mm with a scale and magnifying glass. At least five replicates of each essential oil and control were run and the experiment was conducted in a duplicate.

2.8

2.8 Data analysis

For all bioassays at least five replicates were used and average results presented. In case of>20% insect mortality in control replicates the experiment was repeated, however, in case of 1–20% insect mortality in control replicates Abbott’s formula was used to calculate observed corrected mortality (Abbott, 1925). The lethal doses (LD50 and LD90) of essential oils were calculated by using probit analysis (Finney, 1971). In order to find the statistical difference between bioactivity of different essential oils, the data were analyzed by one way ANOVA (analysis of variance) with a Bonferroni post hoc test. The data of two separate experiments were analyzed using a t test. The statistical tests, probit analysis and relative median potency analysis were performed by using computer software SPSS 20 (IBM, USA). The lethal dose estimates for tested essential oils were considered significantly different (P < 0.05) from the baseline essential oil if confidence limits for relative median potency ratios did not overlap with the value 1 (Gaire et al. 2019).

3

3 Results

3.1

3.1 Yield of essential oils

The highest yield of essential oil was obtained from T. minuta (0.61%) whereas aerial parts of C. ambrosioides had the least amount (0.11%; Table 1).

3.2

3.2 Chemical composition of essential oils

A number of major compounds were found in the essential oil of C. sumatrensis, including 37.7% cis-lachnophyllum ester, 21.6% limonene, 13.4% germacrene D, 6.6% trans-β-farnesene and 5.7% trans-β-ocimene, representing 85.0% of the essential oil (Table 2). In the E. canadensis essential oil sample, limonene (43.4%), germacrene D (12.9%), matricaria ester (9.6%) trans-β-ocimene (7.7%), and cosmene (7.1%) were the major constituents, representing 80.7% of the essential oil (Table 2). cis-β-Ocimene (26.3%), dihydrotagetone (9.9%), cis-tagetenone (15.8%), and trans-tagetenone (19%) were identified as the major constituents in the essential oil of T. minuta (Table 2). The major compounds in the C. ambrosioides essential oil were α-terpinene (41.4%), p-cymene (14.7%), and germacrene D (16.2%).

Table 2 Percentage chemical composition of plant essential oils based on total ion monitoring GC–MS analysis.
Compound RI C. ambrosioides C. sumatrensis E. canadensis T. minuta
Mono-terpene hydrocarbons
β-Pinene 973 4.9 3.1
β-Myrcene 991 3.1 1.3 2.5 1.1
α-Terpinene 1016 41.4
p-Cymene 1024 14.7
Limonene 1028 2.3 21.6 43.4 6.8
cis-β-Ocimene 1037 26.3
trans-β-Ocimene 1048 5.8 5.7 7.7
Cosmene 1130 7.1
Dihydrotagetone 1053 9.9
trans-Tagetone 1144 5.1
cis-Tagetone 1153 6.9
cis-Tagetenone 1232 15.8
trans-Tagetenone 1241 19.4
Carvenone oxide 1258 2.9
Isopiperitenone 1271 3.8
Bornyl acetate 1287 2.3
Limonene diepoxide 1306 5.3
Sesquiterpene
β-Caryophyllene 1425 1.7 1.8 1.1
α-Bergamotene 1438 3.1
trans-β-Farnesene 1457 6.6 1.2
Germacrene D 1486 16.2 13.4 12.9
Elixene 1501 5.3
Esters
cis-Lachnophyllum ester 1511 37.7 5.9
Matricaria ester 1527 9.6
Total mono-terpenes 77.8 33.5 63.8 95.1
Total sesquiterpenes 17.9 27.1 18.3
Total esters 37.7 15.5
Total Identified 95.7 98.3 97.6 95.1

* Retention index (RI) was calculated on DB-5 column. The compounds having peak area > 1% are included in the above table.

3.3

3.3 Insecticidal activity through treated grains

The food poisoning insecticidal bioassay revealed that the bioactivity of essential oils was both dose- and time-dependent. At a dose of 40 mg, C. sumatrensis essential oil showed 56 ± 1.6% and 100.0% mortality of T. castaneum adults after 24 h and 48 h that was significantly greater (P < 0.05) than other three essential oils (Fig. 1). However, when the exposure time increased to 72 h, all tested essential oils exhibited 100% mortality against T. castaneum, similar to the positive control (P > 0.05). On testing the 20 mg dose and 72 h exposure time, C. sumatrensis and E. canadensis essential oils exhibited mortality comparable to the positive control (P > 0.05), whereas C. ambrosioides and T. minuta showed 84.0 ± 1.6% and 88.0 ± 2.5% mortality, respectively, which were significantly lower than (P < 0.05) positive control (Fig. 1).

Mortality percentages of T. castaneum exposed to 10 g of rice grains treated with different concentrations of C. ambrosioides, C. sumatrensis, E. canadensis, T. minuta essential oils and chlorpyrifos for different periods of time. Columns bearing different lower case letters are significantly different (P < 0.05) from each other when the mortality percent of different substances were compared with each other at the same tested dose independent of exposure time by ANOVA post-hoc Bonferroni test. The error bars denote standard error of the mean (n = 5).
Fig. 1
Mortality percentages of T. castaneum exposed to 10 g of rice grains treated with different concentrations of C. ambrosioides, C. sumatrensis, E. canadensis, T. minuta essential oils and chlorpyrifos for different periods of time. Columns bearing different lower case letters are significantly different (P < 0.05) from each other when the mortality percent of different substances were compared with each other at the same tested dose independent of exposure time by ANOVA post-hoc Bonferroni test. The error bars denote standard error of the mean (n = 5).

C. ambrosioides showed 44.0 ± 1.6%, 69.3 ± 2.6%, and 100.0% mortality at the 40 mg dose after 24 h, 48 h, and 72 h exposure time, respectively, whereas at the 10 mg dose the mortality was only 4.0 ± 1.6%, 11.0 ± 0.6%, and 37.0 ± 2.6%, respectively (Fig. 1). C. sumatrensis essential oil showed the highest insecticidal activity against T. castaneum, exhibiting 100% insect mortality after 48 h and 72 h exposure time when 40 mg and 20 mg doses were administrated, respectively. At a dose of 10 mg this essential oil showed 16.0 ± 1.6%, 57.0 ± 1.6%, and 95.3 ± 2.4% mortality after 24 h, 48 h, and 72 h, respectively (Fig. 1).

E. canadensis essential oil at the 40 mg dose exhibited 46.6 ± 2.1, 84 ± 1.6, and 100.0% mortality of T. castaneum after 24 h, 48 h, and 72 h exposure time, respectively. This oil killed 97.3 ± 1.6% and 100.0% of the insects at 20 mg and 40 mg doses, respectively, but only at the longer exposure time (Fig. 1). Although T. minuta essential oil showed relatively good insecticidal activity at the highest tested dose and the longest exposure time, it failed to control T. castaneum at lower doses and shorter exposure times (Fig. 1).

Overall all the tested essential oils exhibited low activity after 24 h exposure time, thus the LD50 of all oils was in the range of 33.9 – 44.8 mg/10 g rice (Table 3). After 48 h exposure, the LD50 and LD90 of C. sumatrensis essential oil against T. castaneum were 7.5 mg and 27.4 mg, respectively, and these values differed significantly (P < 0.05) from the lethal dose determined for other plant essential oils (Table 3 & Table S-1b). The essential oils of C. ambrosioides and T. minuta exhibited similar LD50 and LD90 values (P > 0.05), whereas E. canadensis lethal doses were significantly different (P < 0.05) from the other three oils (Table 3, Table S-1b).

Table 3 Toxicity (LD50 and LD90) of essential oils treated rice against T. castaneum.
Substance Exposure time (h) LD50 mg/10 g rice
(95% FL*)
LD90 mg/10 g rice
(95% FL)
Slop ± SE ╫χ2 (df)
C. ambrosioides 24 43.63 (29.60–146.9)a 127.5 (62.53–2629.1) a 2.75 ± 0.90 0.160 (3)
C. sumatrensis 33.91 (21.57–94.88)a 126.9 (66.45–2237.0) a 1.93 ± 0.52 0.450 (3)
E. canadensis 41.06 (27.14–127.0)a 139.1 (64.70–2317.3) a 2.42 ± 0.73 0.418 (3)
T. minuta 44.78 (29.68–163.3)a 138.5 (65.09–3280.1) a 2.61 ± 0.85 0.322 (3)
Chlorpyrifos < 2.5 < 2.5
C. ambrosioides 48 24.72 (18.45–37.12)c 63.16 (40.75–183.2) c 3.14 ± 0.74 0.852 (3)
C. sumatrensis 7.500 (5.060–10.65)a 27.41 (17.49–68.11) a 2.27 ± 0.47 1.337 (3)
E. canadensis 14.42 (10.22–21.64)b 42.94 (31.39–147.7) b 2.30 ± 0.46 0.277 (3)
T. minuta 22.28 (17.05–30.27)c 48.87 (34.66–105.3) c 3.75 ± 0.85 2.204 (3)
C. ambrosioides 72 11.72 (9.20–14.95)b 22.31 (17.03–37.76) b 4.58 ± 0.94 0.182 (3)
C. sumatrensis 3.670 (2.370–4.880)a 8.930 (6.440–18.57) a 3.32 ± 0.82 0.198 (3)
E. canadensis 5.590 (4.010–7.470)a 14.53 (10.30–28.27) a 3.09 ± 0.63 0.168 (3)
T. minuta 11.89 (9.450–15.04)b 21.17 (16.44–35.19) b 5.12 ± 1.10 0.214 (3)

LD50 Lethal dose to kill 50% adult population. LD90 Lethal dose to kill 90% adult population. * 95% Fiducial limits. ╫ Chi square (degree of freedom). LD50 and LD90 values with different letters indicate significant difference based on relative median potency analysis of essential oils (Table S-1). Lethal doses of essential oils were compared with each other on separate exposure times independently.

When the exposure time increased to 72 h, the essential oil from C. sumatrensis exhibited 3.7 mg and 8.9 mg LD50 and LD90 values, respectively, against T. castaneum which were similar (P > 0.05) to E. canadensis and significantly different from C. ambrosioides and T. minuta (Table 3, Table S-1c). The LD50 and LD90 values of T. minuta and C. ambrosioides were similar (P > 0.05) and the highest among all plants tested (Table 3). Based on relative median potency analysis the most toxic essential oil was C. sumatrensis, whereas C. ambrosioides exhibited the least activity against T. castaneum adults (Table S-1).

3.4

3.4 Insecticidal activity through fumigation

The fumigation bioassay revealed that the essential oils from all plants showed good to excellent bioactivity against adult T. castaneum but only at the higher tested concentration. E. canadensis and C. sumatrensis exhibited 100% mortality at 40 mg/L, which was significantly higher (P < 0.05) than other two essential oils but similar to positive control (P < 0.05). C. sumatrensis vapors exhibited excellent bioactivity among all the tested essential oil to 10 mg/L and thus showed significantly higher activity (P < 0.05) compared to other oils (Fig. 2). In the fumigation bioassay the LD50 and LD90 values exhibited by C. sumatrensis were 6.6 mg/L and 15.8 mg/L, respectively, which were significantly lower (P < 0.05) than all tested essential oils (Table 4, Table S-2). The LD50 and LD90 values of E. canadensis were 10.6 mg/L and 29.6 mg/L, respectively, which were significantly higher than C. canadensis and significantly lower than C. ambrosioides and T. minuta (Table 4, Table S-2).

Mortality percentages of T. castaneum exposed to the vapors of different concentrations of C. ambrosioides, C. sumatrensis, E. canadensis, and T. minuta essential oils and chlorpyrifos for 72 h. Columns bearing different lower case letters are significantly different (P < 0.05) from each other when the mortality percent of different substances were compared with each other at the same tested dose by ANOVA post-hoc Bonferroni test. The error bars denote standard error of the mean (n = 5).
Fig. 2
Mortality percentages of T. castaneum exposed to the vapors of different concentrations of C. ambrosioides, C. sumatrensis, E. canadensis, and T. minuta essential oils and chlorpyrifos for 72 h. Columns bearing different lower case letters are significantly different (P < 0.05) from each other when the mortality percent of different substances were compared with each other at the same tested dose by ANOVA post-hoc Bonferroni test. The error bars denote standard error of the mean (n = 5).
Table 4 Fumigation toxicity (LD50 and LD90) of essential oils against T. castaneum at 72 h exposure.
Substance LD50 mg/L (95% FL*) LD90 mg/L (95% FL) Slop ± SE ╫ χ2 (df)
C. ambrosioides 21.52 (15.53–33.84) c 68.03 (40.78–218.6) c 2.56 ± 0.57 0.315 (3)
C. sumatrensis 6.620 (4.940–8.730) a 15.83 (11.43–29.25) a 3.39 ± 0.67 0.309 (3)
E. canadensis 10.60 (7.850–14.50) b 29.14 (19.99–59.22) b 2.92 ± 0.55 1.329 (3)
T. minuta 17.21 (12.46–25.60) c 53.03 (34.19–149.7) c 2.54 ± 0.52 0.150 (3)
Chlorpyrifos < 2.5 < 2.5

D50 Lethal dose to kill 50% adult population. LD90 Lethal dose to kill 90% adult population. * 95% Fiducial limits. ╫ Chi square (degree of freedom). LD50 and LD90 values with different letters indicate significant difference based on relative median potency analysis of essential oils (Table S-2). Lethal doses of essential oils were compared with each other independently.

3.5

3.5 Anti-fungal activity

The essential oils extracted from C. ambrosioides and E. canadensis exhibited the highest activity against A. flavus, showing 15.7 mm and 16.5 mm zones of inhibition, respectively. C. sumatrensis essential oil was found to be the least active against A. flavus with a significantly smaller (P < 0.05) zone of inhibition against A. flavus (Fig. 3).

Antifungal activity of different test substances against A. flavus. Different alphabets (a-e) indicate significant differences (P < 0.05) when comparison was made between anti-fungal activity of different treatments by ANOVA post-hoc Bonferroni test. The error bars denote standard error of the mean (n = 5).
Fig. 3
Antifungal activity of different test substances against A. flavus. Different alphabets (a-e) indicate significant differences (P < 0.05) when comparison was made between anti-fungal activity of different treatments by ANOVA post-hoc Bonferroni test. The error bars denote standard error of the mean (n = 5).

Insecticidal and anti-fungal bioassays were repeated twice by using the same numbers of replicates, however, no significant difference (P > 0.05, t-test) was found between the results of the two independent experiments.

4

4 Discussion

Essential oils are composed of volatile lipophilic small organic molecules. In the current study, essential oils were extracted from fresh aerial parts of four wild grown plants and among them T. minuta was found to be the richest in essential oil. C. sumatrensis and E. canadensis produced moderate yields, whereas C. ambrosioides yielded least amount of oil. The percentage yield of T. minuta was found to be a bit lower than a study reported from Argentina (López et al. 2011), but quite higher than a Kenyan study that reported a 0.06% yield (Gakuubi et al. 2016). Though the percentage yield of C. ambrosioides essential reported here is comparatively low, it was in accordance with a study from Cameroon (Chekem et al. 2010) that reported 0.12% yield from fresh aerial plants. The percent yields of C. sumatrensis and E. canadensis essential oils were a bit higher than our previous study (Azeem et al. 2019) that described 0.21% and 0.22%, respectively. The quantity and chemical composition of essential oil depends upon a number of biotic and abiotic factors, such as the plant species, the part of plant used, and the condition of plant sample.

GC–MS analysis of the C. ambrosioides sample revealed the presence of α-terpinene, p-cymene, germacrene D, and trans-β-ocimene. The chemical constituents and their abundance in the essential oil of C. ambrosioides varied significantly from a Brazilian report where ascaridole (61.4%), trans-ascaridole (18.6%), and carvacrol (3.9%) were presented as the major constituents (Jardim et al., 2008). α-Terpinene, α-terpinyl acetate, p-cymene (Onocha et al., 1999), and ascaridole (Gupta et al., 2002; Muhayimana et al., 1998) were listed as major constituents in the essential oils of the same species from Nigeria, Rwanda, and India, respectively. The major compound, α-terpinene, in the aforementioned studies was analogous to our findings, although differing in relative abundance. A number of studies demonstrated the presence of different chemotypes of a plant species (Chauhan et al., 2011; Keefover-Ring et al., 2009). Previous studies, as well as our results, indicate the presence of two chemotypes of C. ambrosioides. One is characterized by a high proportion of ascaridole (Jardim et al., 2008), whereas the other has α-terpinene as a major compound (Chekem et al., 2010; Onocha et al., 1999). The chemical difference among the same species might be due to seasonal variation, plant maturity, growing conditions, time of harvest, the plant part used and the drying and post-harvest storage conditions (Anwar et al., 2009; Hussain et al., 2010) or genetic differences (Vernet et al., 1986).

The most abundant compounds in C. sumatrensis essential oil were cis-lachnophyllum ester, limonene, germacrene D, trans-β-farnesene, and trans-β-ocimene. A previous study reported that essential oil extracted from C. sumatrensis grown in France was dominated by trans-β-farnesene (17%), germacrene D (13.6%), limonene (23.2%), trans-β-caryophyllene (10.5%) and cis-lachnophyllum ester (5.9%) (Boti et al., 2007). However in a Brazilian C. canadensis sample, Machado et al. (1995), determined lachnophyllum ester (43.7%), limonene (22.9%), β-farnesene (5.25%), and trans-β-ocimene (4.98 %) as the major constituents. The chemical composition of C. canadensis essential oil determined in the current study was similar to that of the Brazilian plants and differed substantially from the French plant samples.

The chemical analysis of E. canadensis essential oil revealed the presence of limonene, germacrene D, matricaria ester, trans-β-ocimene, and cis-lachnophyllum ester as main compounds. Tzakou et al. (2012) studied the chemical composition of essential extracted from fresh Conyza canadensis (syn: Erigeron canadensis) plants at different stages and reported 50% limonene, 7.5% trans-β-ocimene and 7.9% matricaria ester in the vegetative plant stage. Another similar study from Poland reported 57.9% limonene, 9.1% trans-β-ocimene, 11.1% cis- β-farnesene, 8.5%, trans-α-bergamotene, and 3% trans-β-farnesene (Lis et al. 2003). The major compounds E. canadensis essential oil reported here and in previous studies are quite similar but differ in relative proportion. This might be due to different climate, soil type and other factors that affect composition of plant secondary metabolites (Hussain et al., 2010; El-seedi et al. 2017).

T. minuta essential oil studied here contained cis-β-ocimene, cis-tagetenone, trans-tagetenone, and dihydrotagetone. The essential oil distilled from T. minuta collected from different countries had the same major components in common, including the 2,6-dimethyloct-7-en-4-one molecular structure type and differing in the number of double bonds. We determined that 2,6-dimethyloct-7-en-4-ones in the essential oil of our sample contained three double bonds, which were identified as trans-, and cis-tagetenones, contributing 19.4% and 15.8% of the total sample composition, respectively. The essential oil of T. minuta collected from India contained trans- and cis-tagetenones (14.83% and 9.15%, respectively), cis-tagetone (8.78%) having two double bonds and mono-unsaturated dihydrotagetone (15.43%) (Singh et al., 1992). Likewise, essential oil of the same species collected from Argentina and Iran contained cis-tagetone (62.4% and 61.1%) and dihydrotagetone (10.3 and 33.9%), respectively (López et al., 2011; Shirazi et al., 2014).

The red flour beetle and A. flavus are economically very important pests of stored grains and their products throughout the world. The contamination from these pests not only reduces the nutritional value of food commodities but also makes them unsafe for consumption as food or feed. The use of synthetic pesticides and fumigants is common to protect stored products from infestation of these pests pose adverse impacts on the environment. Plant- based products are considered relatively safe to be used as insect repellents and insecticides against domestic and agricultural pest insects (Isman, 2006). In the present study, the insecticidal and antifungal potential of essential oils from four wild growing plants against T. castaneum and A. flavus was studied. All the tested plants’ essential oils showed insecticidal activity against the adult beetles, however, their bioactivity reduced when applied at the lower dosage and shorter period of time.

The essential oil extracted from C. sumatrensis showed excellent insecticidal activity compared to other three essential oils. The major compounds of C. sumatrensis essential oil were cis-lachnophyllum ester, limonene and germacrene D, which could be responsible for the higher bioactivity. In a previous study limonene was reported to have insect repellent activity against Hylobius abietis (Nordlander, 1990). However, the contribution of the other constituents of the essential oil towards bioactivity cannot be ruled out. A study from Tunisia reported that the essential oil of this plant species showed good anti-bacterial activity (Mabrouk et al., 2013), however, the major compounds differ from those determined in the current study. The essential oil of this plant exhibited slight repellency towards Aedes aegypti mosquito (Azeem et al., 2019), where the chemical composition was quite similar. A recent study from Brazil reported a good allelopathic activity of C. sumatrensis extracts against Biden pilosa (Ferreira et al., 2020). Nevertheless, another recent study from Nigeria described very little insecticidal bioactivity of C. sumatrensis extracts against T. castaneum (Ikpefan et al., 2020). The difference of activity could be explained by differences in bioassay mode and the sample type, i.e. extracts were used by Ikpefan et al. through contact bioassay, whereas essential oil from the aerial part of the plant was tested through food poisoning plus contact assay as well as fumigation in the present study.

In the treated grain assay the essential oil extracted from E. canadensis showed moderate activity after 24 and 48 h and thus showed relatively higher LD50 value compared to C. sumatrensis. On increasing the exposure time this plant essential oil showed activity comparable to C. sumatrensis. In the fumigation bioassay, this plant essential oil showed moderate activity after 72 h exposure time. Interestingly, the essential oil of E. canadensis showed greater mosquito repellent activity compared to C. sumatrensis (Azeem et al. 2019). But in the current study C. sumatrensis was found better against T. castaneum. Moreover, E. canadensis oil was found more active in food poisoning and contact assay compared to fumigation assay.

The essential oil extracted from C. ambrosioides and T. minuta showed low to good activity against T. castaneum after 48 h exposure time, however, these plants exhibited moderate to good LD50 after 72 h of exposure time, when the LD50 of both C. ambrosioides and T. minuta was 11.7 and 11.9 mg respectively. The toxicity of T. minuta oil was moderate to low and was in accordance with a previous report from Pakistan (Shahzadi et al., 2010) where T. minuta seed oil was tested through contact bioassay against T. castaneum. A previous study from our group described low to moderate repellent activity of C. ambrosioides and T. minuta against Ae. aegypti (Azeem et al., 2019).

In this study two different bioassays were employed to test the activity of selected essential oils against T. castaneum. The treated grain bioassay revealed that the tested essential oils were highly lethal against insects even at lower concentrations, however, the same oils showed relatively lower insecticidal activity when tested through fumigation assay. This indicates that the compounds present in the active essential oils possessed higher contact or digestion toxicity compared to fumigation toxicity. Our study results are similar to previously reported data that showed LD50 of fumigation assay was higher than contact (Abou-Taleb et al., 2016; Cardiet et al., 2012; Kumar and Shekhar Mathela, 2017) or ingestion assays (Hashem et al., 2018; Hematpoor et al., 2018). Interestingly, both active essential oils C. sumatrensis and E. canadensis contained high proportions of cis-lachnophyllum ester and matricaria ester which could be responsible for their higher contact or ingestion toxicity. In a previous study, Erigeron annuus essential oil and its major compound, cis-lachnophyllum ester, exhibited excellent insecticidal activity against Lipaphis erysimi (Kumar and Shekhar Mathela, 2017). Another study showed the cytotoxic activity of cis-lachnophyllum ester against MDAMB-231 cells (Satyal et al. 2015).

In contrast to low insecticidal activity against T. castaneum, the essential oils of C. ambrosioides and E. canadensis exhibited strong growth inhibition in an anti-fungal bioassay against A. flavus. The good activity of C. ambrosioides and E. canadensis essential oils against A. flavus could be attributed due to the presence of high proportion of α-terpinene and limonene, respectively. A study from Thailand found excellent anti-fungal activity of limonene against A. flavus (Rammanee & Hongpattarakere, 2011). Researchers from Cameroon reported that α-terpinene rich C. ambrosioides essential oil exhibited excellent anti-microbial activity against a number of yeast species (Chekem et al., 2009). Though relatively low proportion of limonene was also present in C. sumatrensis essential oils which did not show good activity against A. flavus so synergetic effect of other compounds could not be neglected in case of C. ambrosioides and E. canadensis. Although we did not studied the mode action of essential oils against fungus but previous studies elaborated that the essential oils constituents may alter the hyphal morphology, increase membrane permeability, and disturb cellular ultrastructure which may lead to the abnormalities in many biological functions in fungi (Paul et al., 2011; Wang et al., 2019).

5

5 Conclusion

The present study revealed excellent insecticidal activity of C. sumatrensis against the red flour beetle (T. castaneum), whereas E. canadensis showed the highest anti-fungal activity against A. flavus. The bioactivity of C. sumatrensis and E. canadensis phytochemicals indicates an innovative application of essential oils as bio-pesticides to protect stored grains against T. castaneum and A. flavus. Isolation and identification of potent insecticidal compounds from the essential oils of these species could lead to commercial formulations as environmentally friendly alternatives to synthetic insecticides. Furthermore, development of plant-based low-cost formulations would be significant for farmers, especially in developing countries, for protection of stored grains.

Acknowledgement

The authors extend their appreciation to the Researchers supporting project number (RSP-2021/173), King Saud University, Riyadh, Saudi Arabia. The authors are also thankful to Higher Education Commission (HEC), Pakistan with grants No. 21-18/SRGP/R&D/HEC/2014 and International Foundation for Science (IFS), Sweden with grant No. I-1-F-6041-1 for their generous support to conduct this research work.

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

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Appendix A

Supplementary data

Supplementary data to this article can be found online at https://doi.org/10.1016/j.arabjc.2021.103482.

Appendix A

Supplementary data

The following are the Supplementary data to this article:

Supplementary data 1

Supplementary data 1

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