Lethal concentration 50 (LC50) of the total methanolic extract of
Abstract
The termiticidal activity of methanolic extracts of Senna occidentalis and Tithonia diversifolia leaves was determined on the crop pest termite, Ancistrotermes cavithorax. Both extracts were toxic to termite workers by contact and inhalation. The T. diversifolia extract (LC50 of 29, 76 mg/l) was more toxic than the S. occidentalis extract (LC50 of 84.90 mg/l). The two extracts are not repellent but anti-palatable. To recommend insecticidal plants in the culture medium requires the knowledge of their harmfulness to the environment and mammals. This and the toxicity of its two extracts were determined on female rats Rattus norvegicus. The LD 50 of these two extracts exceeded 5000 mg/kg of body mass. The extracts did not cause any renal or hepatic damage after 14 days. The use of these insecticidal plant extracts can therefore be recommended to farmers.
Keywords
- toxicity
- termites
- mammals
- Tithonia diversifolia
- Senna occidentalis
1. Introduction
Termites are one of the greatest scourges in tropical agriculture and agroforestry [1, 2]. In Côte d’Ivoire, West Africa, they regularly attack and destroy food and industrial crops [3, 4, 5, 6]. To control termite attacks and damage, several methods are used by producers. Among these techniques is the use of chemical inputs [7]. Excessive use of chemical inputs can adversely affect living organisms and their environment [8] with very high repair costs. In sub-Saharan Africa, the potential cost of treating pesticide-related illnesses between 2005 and 2020 is about US$90 billion [9]. These problems with synthetic pesticides have led to the search for new termiticidal substances from plants that are environmentally and human health friendly [5, 10, 11]. Pesticidal plants are toxic to pests and generally less harmful to beneficial insects and the environment [12]. The present study set out to evaluate the insecticidal properties of two common plants in West Africa,
2. Materials and methods
2.1 Plant materials
Fresh leaves of
2.2 Animal material
The pesticide tests were conducted on adult workers of the termite
The acute toxicity tests and the histopathology study were conducted on
2.3 Preparation of extracts
Extracts were prepared according to the method described by Kaushik and Vir [13]. Thus, 30 g of powder from the leaves of each plant was mixed in 1 l of 70% methanol. The resulting mixture was stirred for 48 h at room temperature (25°C) using a magnetic stirrer type IKAMAG RCT (Staufen, Germany). The mixture was filtered three times on Whatman paper (No. 4) and then using cotton. The collected solution was subjected to rotary evaporation with a rotavapor BUCHI R-100/32 to obtain the methanolic extract. This solution was then dried under vacuum.
2.4 Biological tests
2.4.1 Toxicity by contact
The test was carried out in Petri dishes 90 mm in diameter containing 3.5 g of soil moistened with 1 ml of distilled water [14]. Using a micropipette, 10, 20, 50, and 100 μl doses of each extract were deposited and mixed with the soil. After depositing, the dishes are air-dried for 1 h. Fifty adult workers of
LD50 is calculated on the basis of 24-h mortality.
2.4.2 Inhalation toxicity
The inhalation test was performed in a large Plexiglass® box of 180 × 20 × 70 mm height according to the method of Tahiri et al. [14]. Into each large box was introduced a Petri dish containing 3.5 g of soil previously moistened with 1 ml of distilled water. Fifty
2.4.3 Barrier soil test
The barrier soil test was conducted according to the method of Tahiri [11]. Nine plastic boxes (chambers) (diameter 5 × 3.5 cm high), closed with plastic covers, were used per arena. One introduction chamber containing sieved nest soil, four substrate chambers containing nest soil, and four food chambers, each containing two pieces of Whatman no. 4 paper of 4 cm2 were used.
The chambers were connected to each other and to the introduction chamber located in the center of the arena by transparent tubes (7 cm length) (LABELL Ch/Fr), length 49 inches. In each trial, only one substrate chamber per arena was treated as barrier soil (50 g of sand moistened with 7.5 ml of the product) to prevent termites from reaching the food source. The other untreated substrate chambers contained 50 g of sand moistened with 7.5 ml of distilled water.
Three hundred
After 10 days of continuous exposure to the product, surviving workers are counted in all arenas, and their total weight is calculated. The tunneling task and food consumption of workers were compared between treated and untreated insects.
2.4.4 Acute toxicity in female rats
The experiment was conducted according to the European OECD guideline 423 [15]. Nine female rats were divided into three batches of three rats (one control and two treated batch) and used for the experiments. The animals were deprived of food overnight. Prior to the experiment, the animals were provided free access to water. Control animals received ml/100 g body weight of distilled water. Due to the low toxicity of
2.4.4.1 Relative mass of vital organs
At the end of the 14-day test, each animal was weighed and then sacrificed. The kidneys, liver, and heart were removed and weighed. Relative masses were calculated according to the following formula:
2.4.4.2 Hematologic and biochemical examinations
At the time of animal sacrifice, volumes of blood were collected in EDTA tubes and dry tubes for hematologic and biochemical analysis, respectively. The hematologic analysis was performed using a Sysmex XS-500i automated analyzer. The blood count consisted of determining the number of white blood cells (WBC), red blood cells (RBC), and blood platelets (PLT), the hematocrit (HCT) and hemoglobin (HGB), the mean blood volume (MCV), the mean corpuscular hemoglobin (MCH) and the mean corpuscular hemoglobin concentration (MCHC).
Biochemical analysis of blood was performed after centrifugation at 3000 rpm for 4 min. An aliquot of serum was collected in Eppendorf tubes. Urea, creatinine, blood glucose, cholesterol, alanine aminotransferase (ASAT), and aspartate aminotransferase (ALAT) were determined using a HITACHI 704 R (Japan) automated analyzer.
2.4.4.3 Histopathology of the liver, heart, and kidney
During the sacrifice, the liver, heart, and kidney of treated and control rats were removed, rinsed with 9‰ NaCl solution, and then fixed in 10% formalin. Flaps of each organ were arranged in cassettes and successively bathed in 80°, 90°, 96°, and 96° ethanol for dehydration. They were then cleared n toluene I and II for 1, 2, and 2 h and then cleared in a step for 2 h in the same reagent. The cassettes were removed from toluene, drained, and impregnated, respectively, in two liquid kerosene baths (I and II) for 2 and 3 h in an oven at 50°C. The cassettes were then cured in the open air and then in the freezer. Sections of 5 μm were made with a Leica RM 2125 RTS® microtome and then stained with hematoxylin and eosin (H&E). The sections were observed with an Olympus CKX41 microscope (Germany) connected to a computer equipped with Videomet software. Pictures of the different histological sections were taken.
2.5 Statistical analysis
The results were expressed as mean plus or minus standard deviation, compared by the ANOVA test and separated by the Newman–Keuls test at the 5% threshold. The statistical software used was Statistica 7.0.
3. Results
3.1 Toxic effect by contact of the extracts
The results of the contact toxicity test indicate that the methanolic extract of
Percentage mortality as a function of time for the contact toxicity test of the methanolic extract of
The mortality rate of termites increased proportionally with the concentration and time of exposure. Fifty percent (50%) of the mortality of
3.2 Lethal concentrations of extracts
The Probit analysis performed on the basis of 24-h mortality, showed that the amount of the methanolic extract of
Products | LC50 (mg/l) | Boundary below 95% (mg/l) | Borne above 95% (mg/l) |
---|---|---|---|
29.76 | 19.87 | 55.90 | |
84.90 | 37.57 | 426.22 |
3.3 Inhalation toxicity of extracts
After 24 h of inhalation, the mortality rates of 95.99% and 91.66% obtained with the methanolic extract of
3.4 Toxic effect by barrier soil of extracts
In the test and control arenas, after 10 days of continuous exposure of 300 workers to moistened soil, the mortality rates of 88.89 ± 3.37% and 85.33 ± 9.61%, respectively, in the tests with
Soil moistening | Average mortality (%) ± standard deviation |
---|---|
Extract of | 85.33 ± 9.61 a |
Extract of | 88.89 ± 3.37 a |
Distilled water | 26.0 ± 1.85 c |
Soil moistening | Cumulative consumption (mm2) ± standard deviation |
---|---|
Extract of | 08.04 ± 1.82 a |
Extract of | 06.09 ± 1.5 a |
Distilled water | 175.92 ± 8.46 c |
3.5 Mortality and symptoms in female rats
Single-dose oral administration of 2000 mg/kg body weight of methanolic extract of
Rats | Doses (mg/kg) | Number of dead rats | Symptoms |
---|---|---|---|
Lot 1 (Control, n = 3) | 0 | 0 | — |
Lot 2 (EMSO, n = 3) | 2000 | 0 | — |
Lot 3 (EMTD, n = 3) | 2000 | 0 | — |
3.6 Effects of extracts on relative organ mass
There was no significant change in the relative mass of the kidneys, liver, and heart of treated rats compared with the relative mass of the organs of control rats (ANOVA, P > 0.05) (Table 5).
Parameters | Lot 1 control | Lot 2 | Lot 2 |
---|---|---|---|
Kidneys | 0.256 ± 0.005 a | 0.268 ± 0.006 a | 0.256 ± 0.005 a |
Livers | 3620 ± 0.300 a | 3920 ± 0.360 a | 3780 ± 0.270 a |
Heart | 0.351 ± 0.013 a | 0.335 ± 0.003 a | 0.326 ± 0.001 a |
3.7 Effects of extracts on biochemical and hematologic parameters
The urea level of rats treated with methanolic extract of
Parameters | Control (distilled water) | ||
---|---|---|---|
Urea (mmol/l) | 0.37 ± 0.026 | 0.37 ± 0.015 | 0.27 ± 0.023* |
Creatinine (mmol/l) | 3.66 ± 0.33 | 3.33 ± 0.33 | 3,.66 ± 0.33 |
Blood glucose (mmol/l) | 0.97 ± 0.033 | 1.03 ± 0.039* | 0.96 ± 0.045 |
Cholesterol (g/l) | 0.58 ± 0.017 | 0.62 ± 0.014 | 0.56 ± 0.015 |
ASAT (U/I) | 161.5 ± 1964 | 134.7 ± 1.76* | 131.3 ± 1.85* |
ALAT (U/I) | 40.33 ± 0.88 | 38.33 ± 1.20 | 36.33 ± 0.88 |
Parameters | Control (distilled water) | ||
---|---|---|---|
WBC (103/μl) | 19.36 ± 1.16 | 20.08 ± 0.86 | 21.30 ± 1.35 |
RBC (106/μl) | 8100 ± 0.38 | 7120 ± 0.27 | 7515 ± 0.255 |
HGB (g/dl) | 12.93 ± 0.26 | 12.20 ± 0.52 | 12.90 ± 0.7 |
HCT (%) | 38.90 ± 0.83 | 37.70 ± 0.77 | 38.10 ± 0.9 |
MCV (fL) | 51.50 ± 0.81 | 51.53 ± 0.58 | 51.60 ± 0.7 |
MCH (pg) | 17.20 ± 0.23 | 17.13 ± 0.12 | 17.05 |
MCHC (g/dl) | 31.53 ± 0.37 | 32.71 ± 0.32 | 33.00 ± 0.2 |
PLT (103/μl) | 723.7 ± 17.07 | 710.3 ± 16.29 | 705.5 ± 14.5 |
NEUT (%) | 21.45 ± 0.65 | 21.45 ± 0.88 | 21.12 ± 1.34 |
3.8 Effects of methanolic extracts on histological parameters
The histopathological study performed on the liver, kidney, and heart revealed no structural abnormalities (inflammation, hepatic cell necrosis, and apoptosis) in the rats treated with different doses of total methanolic extracts of
4. Discussion
In the laboratory, methanolic extracts of the leaves of
The mortality rate of
The LC50 values confirmed that the methanolic extract of
The mortality of termites recorded during the experiment shows that the biological efficacy of the methanolic extract of
The extracts also seemed to act by inhalation. Indeed, inhalation with the methanolic extract of
For the barrier soil tests, the sensitivity of the
Although termites have penetrated the barrier soil (treated soil), food in the food chamber is not consumed. In nearby untreated food chambers, termite consumption is affected and is much lower than in controls. Zhu et al. [23] and Tahiri [11] showed that other botanical insecticides tested on
The acute in vivo toxicity study of the two plant extracts, 14 days after oral administration of methanolic extracts of
The results obtained in this study corroborate those obtained by other authors on the same plants. Thus, it was shown that the total methanolic extract of
Relative organ weights showed no significant difference from the control at the end of 14 days of treatment. This result suggested that the single dose of 2000 mg/kg body weight of methanolic extracts of
Analysis of biochemical parameters showed that the creatine level of the rats did not change significantly (P ˃ 0.5) compared to the control at the end of 14 days of treatment at the dose of 2000 mg/kg body weight. Only urea level decreased significantly (P ˂ 0.5) in rats treated with methanolic extracts of
ALAT activity also showed no significant change (P ˃ 0.05) with the administration of the methanolic extracts of
Macroscopic and microscopic examinations of the liver, kidney, and heart of animals treated with different doses of methanolic extracts of
5. Conclusion
This toxicity study showed that methanolic extracts of
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