@2024 Afarand., IRAN
ISSN: 2252-0805 The Horizon of Medical Sciences 2016;22(3):221-227
ISSN: 2252-0805 The Horizon of Medical Sciences 2016;22(3):221-227
Effect of Oil Paint Fumes Inhalation on the Level of Serum Thyroid Hormones and Thyroid Stimulating Hormone in Rats
ARTICLE INFO
Article Type
Original ResearchAuthors
Siavashi M. (*)Ahmadi R. (1)
(*) Biology Department, Basic Sciences Faculty, Islamic Azad University, Hamedan Branch, Hamedan, Iran
(1) Biology Department, Basic Sciences Faculty, Islamic Azad University, Hamedan Branch, Hamedan, Iran
Correspondence
Address: Biology Department, Faculty of Basic Sciences, Islamic Azad University of Hamedan, Professor Mussivand Bulverde, Madani Town, Hamedan, IranPhone: +988134494000
Fax: +988134494026
msiavashi80@yahoo.com
Article History
Received: July 23, 2015Accepted: May 10, 2016
ePublished: June 30, 2016
BRIEF TEXT
... [1-2]. Disorders in serum level of thyroid hormones can cause several disruptions [3].
... [4-6] the amount of entry of chemical substances into the body and how the person is exposed to them are among the most important issues on the effect of chemicals on humans. Chemicals can enter the human body in different ways, such as various ways of breathing (entering through respiratory tract), gastrointestinal (entering through the digestive tract) and skin contact. Except for corrosive substances (acids and bases), toxic substances do not usually have harmful effects on the body in the beginning, but they can be a part of physiological processes of the human body including absorption, distribution and storage, transfer and removal. For toxicity, it is essential for the chemical or products resulting from their biological transfers to reach critical areas of the body in a certain time and concentration (particular organs in the body) [7]. ... [8-9].
The study aimed to investigate the effects of inhaling oil paints fumes on serum levels of thyroid hormones in male and female rats.
This is an experimental study which is carried out in laboratory.
This experimental study was performed in 2014 at the Islamic Azad University of Hamedan.
15 male rats and 15 female Wistar rats with the weight range of 200 to 250 grams were bought from Pasteur Institute. The rats were kept at approximately 22 ± 2° C and in 12-hour period of light and darkness (12 hours of darkness and 12 hours of light) considering the beginning of photoperiod at 8 am. Water and food (food prepared specifically for rats by Dam Pars factory; Iran) was available unlimitedly. Clinical studies were frequently performed to detect the common symptoms of pathology.
The animals were randomly divided into 6 groups of 5; two male and female control groups that did not inhale any substance during the experiment, and four one and eight-hour groups of male and female rats which were exposed to the smell of oil paint during the experimental period on a daily basis for one and eight hours, respectively, and inhaled the smell of oil paint. To keep the mice, special aquarium- like glass cages were prepared and the top of the cages were covered with metal meshes and a perforated plate. The interior surface of the cages was covered with straw because the contamination of the rats` inhaled air is more likely due to the sawdust contaminated with microscopic creatures. In order to place the oil paint, glass grids were created in the cage to put the test tube inside it. 133 ml of white oil paint was daily poured into each cylinder (Howie luxury; Iran) which was purchased from paint shop. Because the oil paint loses its main components by storage due to immediate evaporation, the top of the cages were covered with a cloth made of burlap in order to prevent the air from being exchanged inside the cages. In addition, for more precision, the control group was kept in a separate room. After 10 weeks of inhaling the smell of the paint, blood samples were taken in order to measure the intended factors. Animals` blood samples were obtained from 9 am to 12 pm. In order to observe the protocol of animals` rights protection, the method of open heart blood-taking was chosen for rats from among different sampling methods because in this way, first the animal is anesthetized by ether and the blood sample is taken during anesthesia and the animal does not feel any pain. For anaesthetizing, first the rat was placed in a beaker containing cotton soaked in ether and thus it was anesthetized mildly. In this regard, Verburg et al. have shown that this degree of anesthesia does not specifically alter the levels of hormones [10]. After anaesthetizing, the animal was put on the desk backwards, so that the tail is towards the operator. Then the skin of the chest was removed, the chest was split open using scalpel and scissors and the tip of the syringe was quickly entered to the heart's left ventricle from its head. 30 minutes after blood-taking, samples were centrifuged at 3000 rpm for 10 minutes; the serum was isolated and used for measuring the factors. For data analysis, SPSS 20 software package was used. To determine the normality of data distribution, Kolmogorov-Smirnov test was employed. The analyzed data was all normal. The applied statistical test was two-way ANOVA and Tukey test was used to analyze the differences between two groups. The results were presented as mean.
The mean of triiodothyronine hormone`s serum level (T3) had a significant reduction in both sexes compared to the control group (p<0.001), so that the process declined more rapidly through increasing the duration of inhaling fumes of the paint, and the serum level mean of T3 hormone revealed a significant decrease in eight-hour group compared to one-hour group in males (p<0.001) and females (p<0.05). The decreasing process was more tangible in females than in males, such that there was a significant difference between the two sexes in one-hour (p<0.001) and eight-hour inhalation groups (p<0.05) (Figure 1). Serum level mean of thyroxine hormone (T4) had a significant reduction in the studied groups compared to the control group (p<0.001) and the more the duration of being exposed to paint fumes increased, the more the decrease in males (p<0.001) and females (p<0.01) was. The decreasing process was more in females than in males and this difference was significant only in one-hour inhalation group (p<0.001; Figure 2). The serum level mean of thyroid-stimulating hormone (TSH) increased through boosting the hours of inhaling paint fumes leading to significant changes compared to the control group (p<0.001). On the other hand, this increasing process was more in female rats and this increase was significant in the group inhaling the paint for 8 hours compared to the male group (p<0.01; Figure 3).
... [10-13] .The lead increases the activity of monoamine oxidase and acetylcholinesterase. These results suggest that lead damages the normal activity of the brain neurotransmitters [14]. ... [15-17]. Heavy metals and paint solvent existing in the oil paint fumes can cause oxidative stress in the cells of the thyroid gland, such that these compounds reduce the amount of thyroid hormones through lipid peroxidation of thyroid gland cells as well as disrupting the function of these cells, and make trouble for the function of this gland [18] ... [19-23].
Future cellular and molecular studies, particularly in the field of the mechanism of oil paint fumes` effects on serum levels changes of thyroxine and triiodothyronine is a favorable research to achieve the mechanism of the impact of oil paint fumes on the performance of thyroid hormones` serum level.
This research has limitations regarding the levels of molecular and cellular studies.
Inhaling the fumes of oil paint decreases the function of thyroid gland and the serum levels of T3 and T4 thyroid hormones while it increases the serum level of TSH and this effect is greater in females.
This study has been supported by research deputy of Islamic Azad University of Hamedan. Many regards are addressed to their efforts.
Non-declared
This study has observed the protocol of animals’ rights protection.
This research has been financially supported by the research deputy of Islamic Azad University of Hamadan.
TABLES and CHARTS
Show attach fileCITIATION LINKS
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[2]Burel C, Boujard T, Kaushik SJ, Boeuf G, Mol KA, Van der Geyten S, et al. Effects of rapeseed meal-glucosinolates on thyroid metabolism and feed utilization in rainbow trout. Gen Comp Endocrinol. 2001;124(3):343-58.
[3]Kinne A, Schülein R, Krause G. Primary and secondary thyroid hormone transporters. Thyroid Res. 2011;4(Suppl 1):S7.
[4]Eissenberg T, Shihadeh A. Waterpipe tobacco and cigarette smoking: Direct comparison of toxicant exposure. Am J Prev Med. 2009;37(6):518-23.
[5]Costanza M, Musio S, Abou-Hamdan M, Binart N, Pedotti R. Prolactin is not required for the development of severe chronic experimental autoimmune encephalomyelitis. J Immunol. 2013;191(5):2082-8.
[6]Vaziri ND, Ding Y. Effect of lead on nitric oxide synthase expression in coronary endothelial cells: Role of superoxide. Hypertens. 2001;37(2):223-6.
[7]Arnold E, Thebault S, Baeza-Cruz G, Arredondo Zamarripa D, Adán N, et al. The hormone prolactin is a novel, endogenous trophic factor able to regulate reactive glia and to limit retinal degeneration. J Neurosci. 2014;34(5):1868-78.
[8]Vigeh M, Smith DR, Hsu PC. How does lead induce male infertility?. Iran J Reprod Med. 2011;9(1):1-8.
[9]Mokhtari M, Shariari M, Goshmardi N. Effect of lead on thyroid hormones and liver enzymes in adult male rats. Hormozgan Med J. 2007;11(2):115-20. [Persian]
[10]Vreeburg JT, Samaun K, Verkade HJ, Verhoef P, Ooms MP, Weber RF. Effects of corticosterone on the negative feedback action of testosterone, 5 alpha- dihydro testosterone and estradiol in the adult male rat. J Steroid Biochem. 1988;29(1):93-8.
[11]Iyer RS, Scott JA. Power station fly ash-a review of value-added utilization outside of the construction industry. Resour Conserv Recycl. 2001;31(3):217-28.
[12]Ford MD, Delaney KA, Ling LG, Erickson T. Toxicology. Philadelphia: W.B. Saunders; 2001. pp. 133-44.
[13]Lau YS, Camoratto AM, White LM, Moriarty CM. Effect of lead on TRH and GRF binding in rat anterior pituitary membranes. Toxicol. 1991;68(2):169-79.
[14]Olney JW. New Insights and New Issues in Developmental Neurotoxicology. Neurotoxicology. 2002;23(6):659-68.
[15]NourEddine D, Miloud S, Abdelkaader A. Effect of lead exposure on dopaminergic transmission in the rat brain. Toxicol. 2005;207(3):363-8.
[16]Zhang F, Degitz SJ, Holcombe GW, Kosian PA, Tietge J, Veldhoen N, et al. Evaluation of gene expression endpoints in the context a Xenopus laevis metamorphosis based bioassay to detect thyroid hormone disruptors. Aquat Toxicol. 2006;76(1):24-36.
[17]Veldhoen N, Boggs A, Walzak K, Helbing CC. Exposure to tetrabromobisphenol-A alters TH-associated gene expression and tadpole metamorphosis in the Pacific tree frog Pseudacris regilla. Aquat Toxicol. 2006;78(3):292-302.
[18]Kulikowska-Karpińska E, Moniuszko-Jakoniuk J. Lead and Zinc influence on antioxidant enzyme activity and melondialdhyde concentration in thyroid. Plish J Environ Stud. 2001;10(3):161-5.
[19]Gustafson A, Hedner P, Schutz A, Skerfving S. Occuptional lead exposure and pituitary function. Int Arch Occup Environ Health. 1989;61(4):277-81.
[20]Scott GR, Sloman KA. The effects of environmental pollutants on complex fish behaviour: Integrating behavioural and physiological indicators of toxicity. Aquat Toxicol. 2004;68(4):369-92.
[21]Lazarus JH, Parkes AB, John R, N'Diaye M, Prysor-Jones SG. Endemic goitre in Senegal-thyroid function etiological factors and treatment with oral iodized oil. Acta Endocrinol (Copenh). 1992;126(2):149-54.
[22]Pedraza PE, Obregon MJ, Escobar-Morreale HF, del Rey FE, de Escobar GM. Mechanisms of adaptation to iodine deficiency in rats: thyroid status is tissue specific, Its relevance for man. Endocrinol. 2006;147(5):2098-108.
[23]Knudsen N, Laurberg P, Perrild H, Bulow I, Ovesen L, Jorgensen T. Risk factors for goiter and thyroid nodules. Thyroid. 2002;12(10):879-88.
[2]Burel C, Boujard T, Kaushik SJ, Boeuf G, Mol KA, Van der Geyten S, et al. Effects of rapeseed meal-glucosinolates on thyroid metabolism and feed utilization in rainbow trout. Gen Comp Endocrinol. 2001;124(3):343-58.
[3]Kinne A, Schülein R, Krause G. Primary and secondary thyroid hormone transporters. Thyroid Res. 2011;4(Suppl 1):S7.
[4]Eissenberg T, Shihadeh A. Waterpipe tobacco and cigarette smoking: Direct comparison of toxicant exposure. Am J Prev Med. 2009;37(6):518-23.
[5]Costanza M, Musio S, Abou-Hamdan M, Binart N, Pedotti R. Prolactin is not required for the development of severe chronic experimental autoimmune encephalomyelitis. J Immunol. 2013;191(5):2082-8.
[6]Vaziri ND, Ding Y. Effect of lead on nitric oxide synthase expression in coronary endothelial cells: Role of superoxide. Hypertens. 2001;37(2):223-6.
[7]Arnold E, Thebault S, Baeza-Cruz G, Arredondo Zamarripa D, Adán N, et al. The hormone prolactin is a novel, endogenous trophic factor able to regulate reactive glia and to limit retinal degeneration. J Neurosci. 2014;34(5):1868-78.
[8]Vigeh M, Smith DR, Hsu PC. How does lead induce male infertility?. Iran J Reprod Med. 2011;9(1):1-8.
[9]Mokhtari M, Shariari M, Goshmardi N. Effect of lead on thyroid hormones and liver enzymes in adult male rats. Hormozgan Med J. 2007;11(2):115-20. [Persian]
[10]Vreeburg JT, Samaun K, Verkade HJ, Verhoef P, Ooms MP, Weber RF. Effects of corticosterone on the negative feedback action of testosterone, 5 alpha- dihydro testosterone and estradiol in the adult male rat. J Steroid Biochem. 1988;29(1):93-8.
[11]Iyer RS, Scott JA. Power station fly ash-a review of value-added utilization outside of the construction industry. Resour Conserv Recycl. 2001;31(3):217-28.
[12]Ford MD, Delaney KA, Ling LG, Erickson T. Toxicology. Philadelphia: W.B. Saunders; 2001. pp. 133-44.
[13]Lau YS, Camoratto AM, White LM, Moriarty CM. Effect of lead on TRH and GRF binding in rat anterior pituitary membranes. Toxicol. 1991;68(2):169-79.
[14]Olney JW. New Insights and New Issues in Developmental Neurotoxicology. Neurotoxicology. 2002;23(6):659-68.
[15]NourEddine D, Miloud S, Abdelkaader A. Effect of lead exposure on dopaminergic transmission in the rat brain. Toxicol. 2005;207(3):363-8.
[16]Zhang F, Degitz SJ, Holcombe GW, Kosian PA, Tietge J, Veldhoen N, et al. Evaluation of gene expression endpoints in the context a Xenopus laevis metamorphosis based bioassay to detect thyroid hormone disruptors. Aquat Toxicol. 2006;76(1):24-36.
[17]Veldhoen N, Boggs A, Walzak K, Helbing CC. Exposure to tetrabromobisphenol-A alters TH-associated gene expression and tadpole metamorphosis in the Pacific tree frog Pseudacris regilla. Aquat Toxicol. 2006;78(3):292-302.
[18]Kulikowska-Karpińska E, Moniuszko-Jakoniuk J. Lead and Zinc influence on antioxidant enzyme activity and melondialdhyde concentration in thyroid. Plish J Environ Stud. 2001;10(3):161-5.
[19]Gustafson A, Hedner P, Schutz A, Skerfving S. Occuptional lead exposure and pituitary function. Int Arch Occup Environ Health. 1989;61(4):277-81.
[20]Scott GR, Sloman KA. The effects of environmental pollutants on complex fish behaviour: Integrating behavioural and physiological indicators of toxicity. Aquat Toxicol. 2004;68(4):369-92.
[21]Lazarus JH, Parkes AB, John R, N'Diaye M, Prysor-Jones SG. Endemic goitre in Senegal-thyroid function etiological factors and treatment with oral iodized oil. Acta Endocrinol (Copenh). 1992;126(2):149-54.
[22]Pedraza PE, Obregon MJ, Escobar-Morreale HF, del Rey FE, de Escobar GM. Mechanisms of adaptation to iodine deficiency in rats: thyroid status is tissue specific, Its relevance for man. Endocrinol. 2006;147(5):2098-108.
[23]Knudsen N, Laurberg P, Perrild H, Bulow I, Ovesen L, Jorgensen T. Risk factors for goiter and thyroid nodules. Thyroid. 2002;12(10):879-88.