|Year : 2018 | Volume
| Issue : 4 | Page : 249-252
Gestational toxicity of Calabash chalk (Nzu) in Wistar rats
Jonah Sydney Aprioku, Ezinne Margaret Ogwo-Ude
Department of Experimental Pharmacology and Toxicology, Faculty of Pharmaceutical Sciences, University of Port Harcourt, Port Harcourt, Rivers State, Nigeria
|Date of Submission||06-Dec-2017|
|Date of Acceptance||30-Jun-2018|
|Date of Web Publication||20-Nov-2018|
Dr. Jonah Sydney Aprioku
Department of Experimental Pharmacology and Toxicology, Faculty of Pharmaceutical Sciences, University of Port Harcourt, East-West Road, P. M. B. 5323, Choba, Port Harcourt, Rivers State
Source of Support: None, Conflict of Interest: None
| Abstract|| |
Objective: Calabash chalk (Nzu) is a geophagic material, consumed by many pregnant women and breastfeeding mothers as remedy for morning sickness in most African countries. The present study aims to evaluate the impact of Calabash chalk consumption in pregnant Wistar rats. Materials and Methods: Median lethal dose of Calabash chalk was initially determined in Wistar rats to be >5000 mg/kg po using Lorke's method. Thereafter, 24 pregnant Wistar rats were divided randomly into 3 groups (n = 8) and orally administered 0, 400, or 800 mg/kg of Calabash chalk from gestation day 0 to 20. Maternal body weights were monitored during sample administration. Fetuses were delivered under anesthesia by cesarean section and pregnancy outcome was assessed. Results: Calabash chalk exposure inhibited maternal weight gain. Uterine implantations were absent in 85% of Calabash chalk exposed rats, and the number of implantation sites were decreased (P = 0.0262) in the rest, compared to control. Uterine weight and the number of fetuses formed in uterine horns of Calabash chalk exposed pregnant rats were decreased (P = 0.0204) when compared with control. In addition, there was resorption of pregnancy, abortion (58%), and stillbirth (5%) in Calabash chalk exposed rats, and fetuses delivered were sluggish and pale. Most of these effects observed were dose-dependent. Conclusion: The results suggest that Calabash chalk has a negative relationship with maternal health and pregnancy outcome.
Keywords: Abortion, Calabash chalk, gestation, Nzu, pregnancy outcome
|How to cite this article:|
Aprioku JS, Ogwo-Ude EM. Gestational toxicity of Calabash chalk (Nzu) in Wistar rats. Int J App Basic Med Res 2018;8:249-52
| Introduction|| |
Geophagia (synonymous geophagy, geophagism, and geotragia), the deliberate consumption or crave for eating earth, soil, chalk, or clay is an ancient practice common to both animals and humans., The practice is not limited to any geographic region or sex, but has become a common habit cutting across all social classes., It is highly prevalent in situ ations like poverty and famine to suppress appetite,, and also in some psychiatric conditions like pica, compulsive indiscriminate eating of nonnutritive substances.,,
In most African countries, Calabash chalk or Calabash clay is one of the most common geophagic materials. Popularly called Nzu in Nigeria, Calabash chalk is known as La Craie or Argile in French, and Mabele in Congo. It is found and obtained usually from the soil (mining pits), and occurs naturally as a light brown to almost white solid which is relatively soluble in water. Calabash chalk is marketed in the raw form or processed by combining clay, sand, wood ash or salt; packaged as powder, molded blocks or pellets and is readily available in open shops. It is consumed by many because it is believed to have various ethnobotanical uses. It is used as antacid, antidiarrheal, contraceptive, nutritional supplement, wound healing, and skin beautification agent. It is also used for the treatment of skin diseases, fetal growth and wellbeing during pregnancy, and sociocultural activities. In general, pregnant women gravitate more toward Calabash chalk consumption in humans., They use Calabash chalk as remedy for morning sickness and to satisfy their increased appetite and other peculiar desires.
Being an earth material, Calabash chalk is not unlikely to be contaminated with microorganisms or heavy metals, which may even increase with processing and or storage. Studies on the analysis of Calabash chalk are currently very few, but the available data indicate that it contains heavy metals whose qualitative and quantitative compositions vary with respect to the geographical location of the chalk., However, it is believed that aluminum forms one of the major constituents, probably because of the presence of kaolin clay group in most Calabash clay. Others include, lead, arsenic, and chromium., Recently, the Texas Department of State Health Services and Food and Drug Administration has raised concerns of potential health risks from Calabash chalk consumption, especially by pregnant and breastfeeding women in view of lead and arsenic contamination. This is important especially as pregnancy is a delicate and vulnerable period, and is generally unsafe for many chemicals. An empirical evaluation of the safety or toxicity profile of the consumption of Calabash chalk during pregnancy is thus justified as currently, not much is known about its effect on pregnancy.
The present study aims to determine the effect of Calabash chalk (obtained from Umuahia North in the southeastern part of Nigeria) on maternal and fetal health indices following its exposure throughout the period of gestation in Wistar albino rats.
| Materials and Methods|| |
Sample collection and preparation
Natural Calabash chalk was excavated from a local mining site at Ogbanzu in Ohia, Umuahia North Local Government Area, Abia State, a southeastern state of Nigeria in October, 2016 with the assistance of a local miner and commercial dealer of Calabash chalk in the area. The sample was oven-dried at 110°C, powdered with a mortar and pestle and stored until used for the experiment. The sample was dissolved in distilled water and administered during the experiment.
Acute toxicity study (median lethal dose determination) of Calabash chalk
Three-graded doses of Calabash chalk (1000, 2500, or 5000 mg/kg) were administered to overnight fasted groups of rats (n = 3 per group) by oral gavage. They were observed closely for mortality, behavioral changes and other symptoms of toxicity over a period of 24 h.
Twenty-four sexually mature female Wistar albino rats of body weight 150–170 g and twelve adult male rats of body weight 180–200 g were used in this study. The animals were obtained from the Animal House of our institution. They were maintained with standard rodent diet and water was given ad libitum under natural lighting condition and ambient temperature of 25°C ± 3°C. Animals were handled in accordance with international guidelines and experimental procedures followed the approved guideline of the Ethical Committee on Animal Studies of our institution (UPH/CREC/ERA/328).
Female rats in the estrous phase were mated with male rats (2:1) and examined for the occurrence of pregnancy. The presence of a copulatory plug in female animals confirms pregnancy and the day of observation represents gestation day 0 (GD0). Estrous phase was determined by evaluation of vaginal smear as described by Marcondes et al. Vaginal smears of animals in estrus phase had predominantly cornified cells. Pregnant rats were separated and divided randomly into three groups (I, II, and III) containing eight rats each. Group I rats were given distilled water (1 ml) and served as control. Groups II and III were administered Calabash chalk (400 or 800 mg/kg) once daily. The sample was administered orally by oral gavage from GD0 to GD20. The animals were deeply anesthetized with diethylether (Loba-chemie PVT, Ltd., India) and laparotomized on GD20 (the average gestation period of rats). Fetuses were delivered and their number and physical characteristics in each animal group were recorded. The two horns of the uterus were equally examined to determine the number of implantation sites and presence of resorption sites. After examination, the uterus was weighed and recorded. Before animals sacrifice, maternal body weights of control and experimental rats were recorded on GD0, GD10, and GD20.
Data are expressed as a mean ± standard error of mean. Data were analyzed by one-way analysis of variance followed by Student's t-test for comparison between control and the treated groups using GraphPad Prism Version 5 software (GraphPad Software Inc., San Diego, CA, USA). Values of P < 0.05 were considered statistically significant.
| Results|| |
Acute toxicity study (median lethal dose determination)
There was no mortality after treatment with Calabash chalk, even at the concentration of 5000 mg/kg. In addition, there were no observable behavioral changes or signs of toxicity in all the animals [Table 1]. Thus, lethal dose (LD50) is >5,000 mg/kg, po in rats.
|Table 1: Oral treatment with Calabash chalk over 24 h causes no acute toxicity in rats|
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Effect of Calabash chalk exposure on pregnancy indices
There was statistically significant increase in body weight of rats in control (P < 0.0001) and experimental groups (P = 0.0022, P = 0.0005) at GD10 when compared to GD0 [Figure 1]. Body weight of control rats at GD20 was also higher (P = 0.0026) compared to GD10, but weights of experimental rats at GD20 were not different compared to their weights at GD10 (P = 0.1479, P = 0.7497) [Figure 1].
|Figure 1: Maternal Calabash chalk (Nzu) exposure inhibits gestational weight gain in Wistar albino rats. Data are expressed as mean ± standard error of mean, (n = 8 per group) *P < 0.01, GD0 versus GD10; **P < 0.001, GD0 versus GD10; ***P < 0.0001, GD0 versus GD10 ‡P < 0.01, GD10 versus GD10 GD: Gestation day|
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Furthermore, whereas all control rats showed the presence of fetuses and implantation sites in their uteri, these were observed only in 6 (75%) of 400 mg/kg and 2 (25%) of 800 mg/kg Calabash chalk exposed rats [Table 2]. In addition, the number of fetuses in Calabash chalk exposed mothers were fewer (P = 0.0084, P < 0.0001) when compared to control rats [Table 2] and [Table 3]. Besides, 2 (5%) of the fetuses in 400 mg/kg Calabash chalk treated rats were not alive and were delivered as stillbirths [Table 2]. Number of implantation sites in the Calabash chalk treated rats were also lower (P = 0.0262, P = 0.0004) compared to control rats [Table 2] and [Table 3]. Furthermore, the number of fetuses in the control animals was the same compared to the number of implantation sites, whereas the number of fetuses was fewer in the Calabash chalk exposed animals. This corresponded to 19.2 and 57.9% abortions, respectively, in the exposed rats [Table 2]. Furthermore, resorption of pregnancy was observed in the exposed rats, whereas control rats had zero resorption [Table 2] and [Table 3]. Macroscopical examination of the fetuses after delivery showed that fetuses in all the three groups were active and morphologically normal. However, fetuses of Calabash chalk (800 mg/kg) exposed mothers appeared weak, sluggish and pale [Table 2]. Furthermore, uterine weights of Calabash chalk exposed rats were decreased (P = 0.0204) relative to control rats [Figure 2].
|Table 2: Effect of calabash chalk (Nzu) exposure on pregnancy indices in Wistar albino rats|
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|Table 3: Maternal exposure of calabash chalk (Nzu) in Wistar albino rats affects implantation, and number of fetuses formed|
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|Figure 2: Maternal Calabash chalk (Nzu) exposure reduces uterine weight in Wistar albino rats. Data are expressed as mean ± standard error of mean, (n = 8 per group) *P < 0.05|
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| Discussion|| |
Median LD50 of the sample was determined initially to select suitable (safe) dose levels to be used for the study. LD50 is a fundamental acute toxicity index which measures the potential of a compound to cause lethality in animals and is an important determinant of the safety margin or therapeutic index of a drug. The acute toxicity study showed that Calabash chalk produced no mortality at 5000 mg/kg (i.e., LD50 > 5,000 mg/kg), indicating that the sample is likely to have a high safety margin. The doses used in this study (400 and 800 mg/kg) were much lower than the obtained LD50 value and deliberately selected in consideration of the sensitivity of pregnancy period to chemicals exposure.
From the results, it was observed that Calabash chalk treatment inhibited weight gain in pregnant rats in a dose-dependent manner over the dose range used. Furthermore, its administration resulted in dose-dependent reductions in number of implantations, as well as number of fetuses delivered. All these are serious negative indices of pregnancy, which can independently affect the overall wellbeing of the developing embryo or fetus.,, Implantation of the embryo follows egg fertilization and is essential for embryo development and sustenance of pregnancy. The presence of implantations was observed only in 2 (25%) of the rats that received 800 mg/kg, whereas implantations were retained in six animals (75%) that were administered 400 mg/kg of Calabash chalk. It does appear that Calabash chalk possibly deteriorates or dissolves implantation after pregnancy, i.e., preventing embryo growth. Further, among the exposed rats in which pregnancy progressed, there was 57.9% loss of pregnancy and 5% fetal death (in utero), providing evidence that Calabash chalk has the potential of inducing abortion in animals. This can obviously interfere with the normal sustenance of pregnancy and may support the reported local use of the agent by young girls of reproductive age in rural African communities as contraceptive. Furthermore, Calabash chalk treatment caused a reduction in the uterine weight. This may result from alteration of reproductive hormone secretion and/or activity and can contribute to the poor sustenance of pregnancy that was observed in the treated rats. In addition, it was observed that the fetuses delivered by pregnant rats that were treated with Calabash chalk appeared pale, suggestive of anemia. These results strongly indicate that Calabash chalk consumption during pregnancy can result in negative effects.
| Conclusion|| |
Gestational exposure of Calabash chalk causes negative maternal health consequences and pregnancy outcome in rats.
We would like to thank the laboratory staff of Department of Experimental Pharmacology and Toxicology, University of Port Harcourt, Nigeria, who provided technical assistance.
Financial support and sponsorship
Conflicts of interest
There are no conflicts of interest.
| References|| |
Hawass NE, Alnozha MM, Kolawole T. Adult geophagia – Report of three cases with review of the literature. Trop Geogr Med 1987;39:191-5.
Woywodt A, Kiss A. Geophagia: The history of earth-eating. J R Soc Med 2002;95:143-6.
Abrahams PW, Follansbee M, Hunt A, Smith B, Wragg J. Iron nutrition and possible lead toxicity: An appraisal of geophagy undertaken by pregnant women of UK Asian communities. Appl Geochem 2006;21:98-108.
McLoughlin IJ. The picas. Br J Hosp Med 1987;37:286-90.
Luby J, Joan L. Handbook of Preschool Mental Health Development, Disorders and Treatment. New York: Guilford Press; 2009.
Vermeer DE, Ferrell RE Jr., Nigerian geophagical clay: A traditional antidiarrheal pharmaceutical. Science 1985;227:634-6.
Dominy NJ, Davoust E, Minekus M. Adaptive function of soil consumption: An in vitro
study modeling the human stomach and small intestine. J Exp Biol 2004;207:319-24.
Dean JR, Deary ME, Gbefa BK, Scott WC. Characterisation and analysis of persistent organic pollutants and major, minor and trace elements in calabash chalk. Chemosphere 2004;57:21-5.
Olatunji AS, Olajide-Kayode JO, Abimbola AF. Evaluation of geochemical characteristics and health effects of some geophagic clays Southern Nigeria. Environ Geochem Health 2014;36:1105-14.
Okeke C, Obasi C. Semantic content of Igbo traditional. Int J Linguist Lit 2014;3:47-62.
Wiley AS. Geophagy. Encylopedia of Food and Culture. New York: Charles Scribnesond; 2008.
Lar UA, Agene JI, Umar AI. Geophagic clay materials from Nigeria: A potential source of heavy metals and human health implications in mostly women and children who practice it. Environ Geochem Health 2015;37:363-75.
Yuan Y, Foley GL. Female reproductive system. In: Haschek WM, Rousseaux CG, Wallig MS, editors. Handbook of Toxicologic Pathology. London: Academic Press; 2002.
Lorke D. A new approach to practical acute toxicity testing. Arch Toxicol 1983;54:275-87.
Marcondes FK, Bianchi FJ, Tanno AP. Determination of the estrous cycle phases of rats: Some helpful considerations. Braz J Biol 2002;62:609-14.
LeBeau JE. The role of the LD50 determination in drug safety evaluation. Regul Toxicol Pharmacol 1983;3:71-4.
Vahter M. Effects of arsenic on maternal and fetal health. Annu Rev Nutr 2009;29:381-99.
Aprioku JS, Siminialayi IM. Maternal lead exposure and pregnancy outcome in Wistar albino rats. J Toxicol Environ Health Sci 2013;5:185-93.
Aprioku JS, Ebenezer B, Ijoma MA. Toxicological effects of cadmium exposure during pregnancy in the Wistar albino rat. Toxicol Environ Health Sci 2014;6:16-24.
[Figure 1], [Figure 2]
[Table 1], [Table 2], [Table 3]