Abstract
The present study was designed to determine the lethal dose 50 (LD50) of combination of cypermethrin, a pyrethroid, and endosulfan, an organochlorine compound in Wistar rats. LD50 is the amount (dose) of a chemical, calculated as per the concentration of chemicals that produces death in 50% of a population of test animals to which it is administered by any of a variety of methods. A single oral dose of combination of cypermethrin and endosulfan were dissolved in dimethyl sulfoxide (DMSO) in a ratio of 1:1 and administered orally at the concentration of 165 mg/kg body weight (b.w), 330 mg/kg b.w, 660 mg/kg b.w, and 1320 mg/kg b.w to experimental animals. LD50 was calculated according to the method described by Miller and Tainter (1994) and was observed as 691.83 mg/kg b.w for this combination. Single dose of test article at 165 mg/kg b.w did not reveal any toxic signs or behavioral alterations, hence considered as No observed Adverse Effect level (NOAEL).
Keywords: Cypermethrin, endosulfan, LD50, no observed adverse effect level, organochlorine, pyrethroid
INTRODUCTION
Pesticide, a substance or a mixture of substance used against pests in all developmental forms, have become omnipresent contaminants of environment and are also found in water, soil, air, and both human and animal tissues all over the world.[1,2] The pesticides play a very important role in modern agriculture, particularly in controlling harmful pests and insects with less effort and are cost effective. Pesticides have become an area of intense research due to their diverse properties and related effects. Though the demand for pesticide products and their contribution in aiding agricultural efficiency are clear, but the volume of production indicates that the potential for misapplication and accidental exposure is great. Besides, being beneficial for increased crop yield as well as in vector control programmers, it has resulted in the manifestation of several health-related problems.[3] In order to find new insecticides of low mammalian toxicity, less insect resistance, and low persistence, the number of groups of insecticides have been synthesized and synthetic pyrethroid is the result of one of such attempt.[4]
The toxicity of a pesticide is measured in several ways, but, generally, human toxicity is estimated based on the test results on rats and other animal models. A pesticide that is poisonous for rats is not necessarily equally poisonous to humans or other animals. Some pesticides turn out to be fatal after one large dose (acute toxicity), others can be dangerous after small dose or repeated doses (chronic toxicity). The commonly used term to describe acute toxicity is LD50, where LD means lethal dose deadly amount, and the subscript 50 means that the dose is acutely lethal to 50% of the animals to whom the chemical was administered under controlled laboratory conditions. In other words, LD50 is the statistically derived single dose of a substance that produces death in 50% of a population of test animals to which it is administered by any of the methods like oral, dermal, inhalation, or intravenous. Determination of this test examines the relationship between dose and the most extreme response–death. The more potent or toxic the chemical, lower the LD50 and smaller the dose needed to cause death. Therefore, a pesticide with an oral LD50 of 500 mg/kg would be much less toxic than a pesticide with an LD50 of 5 mg/kg. Normally, LD50 is expressed as milligrams of substance per kilogram of animal body weight (mg/kgbw). It provides information on health hazards likely to arise from short-term exposure. This data serve as a basis for labeling and classification and also helpful in establishing a dosage regimen in sub-chronic and chronic studies.
The LD50 is determined by any accepted methods, e.g. Miller and Tainter,[5] Bliss,[6] Litchfield and Wilcoxon,[7] Finney,[8] Weil,[9] and Thompson.[10]
Previously, single insecticides/pesticides were used in agriculture to control insects, but repeated use of these insecticides has made insects/pests resistant to them. Therefore, to overcome such problems, cocktails of pesticide are prepared by farmers on the suggestion of pesticide sellers in order to get better quality and faster results. These cocktails not only kill the harmful pests but also are very hazardous to both farmers who come in direct contact and common man, who consumes them (through fruits and vegetables).[11,12,13] The combination of pesticides are gaining popularity in pest control programs as they exhibit a broad spectrum of activity coupled with better efficacy and economy.[14]
Synthetic pyrethroid and organochlorine pesticides are nowadays widely used in the agriculture industry to control pests on crops and ectoparasites on livestocks.[15]
Cypermethrin is a neurotoxic synthetic pyrethroid, primarily used as an insecticide and endosulfan is a neurotoxic organo chlorine compound of the cyclodine group, primarily used as an insecticide and secondarily as an acaricide. The oral LD50 of cypermethrin is 250 mg/kg (in corn oil).[16,17] The LD50 of endosulfan varied widely depending on the route of administration, species, vehicle, and sex of the animal.[18] The oral LD50 of endosulfan for rats is 80 mg/kg b.w.[19]
Several independent studies on cypermethrin and endosulfan toxicity have been carried out in different parts of the world. However, no attempts have been made to understand the combined toxic effect of these two pesticides, which is presently being used very commonly in India. Thus, keeping this in mind, the present study was designed to determine the oral median lethal dose of the combination of pesticide endosulfan, an organochlorine compound, and cypermethrin, a synthetic pyrethroid on Wistar rats, using dimethyl sulfoxide (DMSO) as vehicle.
MATERIALS AND METHODS
Test chemicals
Cypermethrin (92.21% pure, liquid) and endosulfan (95.80% pure, solid) were obtained from Hindustan Insecticides Limited (A government of India Enterprises).
Animals and experimental design
A total of 25 healthy adult male Wistar rats (weighing about 200 ± 20 gm) were obtained from Central Animal Facility (All India Institute of Medical Sciences, New Delhi). All animals were allowed to acclimatize to the experimental conditions for a period of 5 days. All the rats were housed in polyacrylic cages, not more than 3 animals per cage, and maintained under standard laboratory conditions (natural light/dark cycle, room temperature 22 ± 3°C). Animals were given standard dry rat pellet diet, and tap water was provided ad libitum. The institutional animal ethics committee approved the experimental protocol.
Dose preparation and administration
Rats were fasted for 18 h prior to dosing. The compound was administered once orally using 22-gauze oral feeding needle to the rats. The volume of the dose depends on the size of the animals. In rodents, it should not exceed 1 ml/100 g b.w.[20,21] In this study, the dose was mixed, i.e., combination of pesticide (endosulfan and cypermethrin, ratio 1:1) in 0.5 ml of DMSO.
Estimation of the dose range and percentage of mortalities
An approximate LD50 can be determined by a so-called “up and down” or the “staircase method” using two animals and increasing the doses of the combination of endosulfan and cypermethrin (ratio 1:1). Five doses were given orally to 5 groups of rats (5 rats in each group) for the determination of LD50 of the combination starting from 0% mortality to 100% mortality[22] [Table 1]. The animals were observed for 2 h and then at 4th, 6th, and 24th h for any toxic signs and symptoms. After 24th h, the numbers of deceased rats in each group were counted and the percentage of mortality was calculated using the graphical method of Miller and Tainter.[5]
Table 1.
RESULTS
Signs recorded during experiment
Initially, the combination of endosulfan and cypermethrin did not produce any significant effect on central nervous system (CNS) at 165 mg/kg. However, when the doses of 330 mg/kg, 660 mg/kg, and 1320 mg/kg were administered, signs of CNS stimulation were observed for 16 to 24 h. The animals exhibited chewing, licking, salivation, tremors, arching and rolling, clonic convulsions, lacrimation, occasional pawing, or burrowing, and coarse whole-body tremors associated with movement of legs. Finally, choreoathetosis developed exhibiting slow writhing and twisting movement of the neck and tail of animals. The animals showed labored breathing, gasping, and death.
Conversion of percentage mortalities to probits and calculation of LD50
The percentage of animals that died at each dose was then transformed to probit [Table 2] using Finney's method[23] [Table 3]. The percentage dead for 0 and 100 were corrected before the determination of probits. For 0% dead: 100 (0.25/n) and for 100% dead: 100 (n − 0.25/n), where n = 5 rats.[24]
Table 2.
Table 3.
The probit values thus obtained were plotted against log-dose and then the dose corresponding to probit 5, i.e., 50%, was found [Figure 1].
In the present study, combination of endosulfan and cypermethrin (ratio 1:1), log LD50 is 2.84 and LD50 is 691.83 mg/kg. The SE of the LD50 was calculated using the following formula.[24]
The probits of 84 and 16 from Table 1 are 5.99 and 4.01 (approximately 6 and 4), respectively. The log-LD values for the probits 6 and 4 are obtained from the line on the graph in Figure 1, which, in the present case, are 3.2 and 2.46, and their antilog are 1584.89 and 288.40, respectively. Using these values in formula (a), the SE of LD50 is 410.28.
Therefore, LD50 of combination of cypermethrin and endosulfan with DMSO, when given orally was observed as 691.83 ± 410.28, with 95% confidence interval of 281.55-1102.11.
DISCUSSION
Pesticides play an important role in modern agriculture by providing dependable, persistent, and relatively complete control against harmful pests with less labor and low cost. They have, no doubt, increased crop yields by killing different types of pests, which are known to cause substantial or total crop damage. At the same time, these chemicals are considered as potent pollutants of the environment with undesirable effects on non-target organisms.[25] Rampant use of pesticides in agricultural products continue to risk the life of the common man. Thus, it is very important to know the LD50 of the pesticide before using it in the fields. Data collected for the MAFF Pesticide Usage Survey of arable crops in England and Wales[26] in 1990 showed that over 25,000 different combinations of two active ingredients were sprayed as tank mixes or co-formulations on the 761 farms surveyed, though only a small proportion were used on significant numbers of farms. A more detailed analysis of spray applications was carried out using data from the 1992 survey of arable crops in England, Scotland, and Wales.[27] This reported tank mixes and co-formulations were applied to 10.9 million ha, implying a mean of over two mixtures per crop. Fifty-nine different combinations of two or more active ingredients were applied to 30,000 ha or more.
Combination of two or more pesticides may have additive, synergistic, or antagonistic effect. Therefore, the present study was conducted to find out the LD50 of the combination of endosulfan and cypermethrin (ratio 1:1). This combination did not show any gross visible changes, and no toxic signs at 165 mg/kg b.w and considered to be the No Observed Adverse Effect Level (NOAEL). However, animals administered with a combination of endosulfan and cypermethrin at the doses of 330 mg/kg b.w, 660 mg/kg b.w, and 1320 mg/kg b.w dose showed a sequence of the signs of toxicity, viz., acute cholinergic symptoms, chewing, licking, salivation, writhing, tremors, arching and rolling, clonic convulsions, lacrimation, occasional pawing, or burrowing, coarse whole-body tremors associated with movement of legs, hyperactivity to sound/touch, abnormal gait pattern, incoordinaton, imbalance, difficulty in breathing, and convulsions immediately after dosing and these symptoms were persisted for 6 h. The pattern of the signs after the administration of combination of endosulfan and cypermethrin is strongly suggestive of CNS toxicity. Similar signs were observed by Nagarjuna et al.,[17] and Manna et al.,[28] while using only cypermethrin and chlorinated hydrocarbons insecticides.[29]
The geographic mean of two doses i.e.: The lowest dose that killed one animal and the highest dose that did not kill any animal determines LD50 of a particular substance. The graphical representation of probit versus log dose showed a typical straight line, which was in agreement with the principle of probit analysis [Figure 1]. According to Miller and Tainter probit analysis method, at 24 h, the acute oral LD50 value of combination of endosulfan and cypermethrin (ratio 1:1) in DMSO was calculated as 691.83 mg/kg b.w (with 95% confidence interval) in the present study, which is 8.64-folds higher (in terms of LD50) than the LD50 values of endosulfan alone and 2.76-folds higher (in terms of LD50) than the LD50 of cypermethrin alone determined using other vehicles like corn oil.[16,17,19] Actual decrease in LD50 or increases in mortality are used to assess the scale of the increase in toxicity following combined exposure and vice versa. Various studies suggests that combination of pesticides always have an additive effect and when two or more pesticides are used together, their toxicity is always more than the toxicity of single pesticide;[30] but, in the present study, increase in LD50 value of combination is seen, indicating that when endosulfan and cypermethrin are used in combination with DMSO, the toxicity of the combination is reduced in Wistar rats. Manna et al.,[28] reported that DMSO also reduces toxicity.
However, published experimental work on cypermethrin and endosulfan toxicity in rat is limited and there is no experimental work reported on the combination of endosulfan and cypermethrin toxicity with DMSO as a vehicle. However, it is concluded that, the overall result of the present study clearly demonstrates that oral LD50 of the combination of endosulfan and cypermethrin (ratio 1:1) with vehicle DMSO is as 691.83 mg/kg b.w (with 95% confidence interval) and NOAEL of the combination of the above mentioned pesticide is 165 mg/kg b.w in Wistar rats.
ACKNOWLEDGMENT
University Grant Commission (UGC) is hereby acknowledged for awarding financial support to conduct this study (SRF-Ms. Jaya Raj).
Footnotes
Source of Support: UGC (University Grant Commission).
Conflict of Interest: None declared.
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