The thyroid gland is regulated by the pituitary gland which secretes thyroid-stimulating hormone (TSH) to produce thyroxine (T3) and triiodothyronine (T4); when the levels of these are sufficient in the blood the pituitary gland detects the levels and then reduces the secretion of TSH and therefore the levels of T3 and T4 are maintained within normal limits, playing a very important role in the organism as they regulate growth and development, cardiac activity and blood pressure and the way in which the body uses and stores energy 1,2,3. One of the most common disorders is hyperthyroidism or thyrotoxicosis, which results from excessive synthesis of thyroid hormone 4. The prevalence of this pathology in the general population is 0.5%, and it occurs more frequently in women than in men. It has been observed that in women it appears between the third and fourth decade, while in men the highest incidence occurs in the last decades of life 5. These patients may present insomnia, irritability, psychomotor agitation, affective lability, memory impairment and in some cases, psychotic symptoms 6,7.
Currently,there are a large number of toxic substances to which we are exposed through environmental pollution, which occurs globally. These substances are toxic not only to humans but also to ecosystems and are used indiscriminately mainly for economic reasons 8. Among these toxic agents are lead and mercury, which are heavy metals with well-known toxic effects. These effects occur due to exposure to these elements or to compounds containing them. However, studies on the effect of Pb and Hg on thyroid function and particularly on TSH and T3 free levels are scarce 9 (Figure 1).
Based on the problems described above, and that currently specialists in cardiology and endocrinology have requested the determination of these metals in this type of patients the present study aimed to evaluate the relationship between the concentration of thyroid stimulating hormone (TSH), free thyroxine (T3F) and free triiodothyronine (T4F) with the levels of lead (Pb) and mercury (Hg) in patients (adults) with suspected hyperthyroidism.
The study sample consisted of 20 individuals of both sexes with a diagnostic impression of possible hyperthyroidism and 20 individuals with no underlying pathology (control group). The following criteria were taken into consideration for sample selection:
Individuals of both sexes willing to participate voluntarily in the study.
Over 18 years of age.
Non-smokers and low or sporadic alcohol consumption.
Individuals suffering from chronic or hematological diseases.
Persons occupationally exposed to heavy metals.
Each individual participating in the study provided a specific urine sample (first-morning, before starting activities), in clean plastic containers, after instructions for correct collection. Samples were refrigerated between 2°C and 8°C and transported to the FITOQUIMICA20 C.A Laboratory.
For blood sample collection, the rules of asepsis and antisepsis were followed. 10 mL of blood was drawn from the antecubital vein with a 12 mL disposable injector and a 21G x 1'' needle. The contents of the injector were then gently transferred into two tubes previously labeled with the patient's data. Five milliliters of blood were placed in a tube with two drops of ethylenediaminetetraacetic acid (EDTA) for Pb analysis. The remainig 5 ml were intended for the analysis of hormones.
It was performed by method cold vapor atomic absorption spectrophotometry, using the method recommended by the National Institute for Occupational Safety and Health (NIOSH), 10. To 4 mL of uncentrifuged urine, 7 mL of 65% nitric acid (HNO3) (Merck KGaA, Germany) was added. After 5 minutes, 60 mL of deionized water was added and, to reduce the mercury ion Hg2+ to its elemental form and initiate the emission of cold vapors, 1 mL of 20% SnCl2 solution prepared from of SnCl2•2H2O ACS 98% (Sigma-Aldrich Co., USA). The absorbance measurement of the samples at 253.7 nm (maximum absorption at the mercury resonance line) was performed with a Bacharach® MAS-50B cold vapor spectrophotometer. A calibration line was elaborated using a mercury chloride standard in a range of concentrations from 0.2 to 3 µg/dL.
Creatinine analysis by the modified Jaffe method is based on reacting the sample with sodium picrate, in an alkaline medium, to form a red chromogen with an absorption maximum at 510 nm 11. Analytical results are frequently expressed in micrograms of mercury per gram of creatinine. The method consists of diluting the urine sample with distilled water (1/100) to a final volume of 5 mL. An aliquot of 0.5 mL of sample was taken, 0.5 mL of distilled water and 2 mL of alkaline picrate were added. The latter reagent was prepared by mixing 20 mL of a saturated aqueous solution of ACS 99% picric acid (Merck KGaA , Germany) and 4 mL of 10% NaOH ACS 97% (Sigma-Aldrich Co., USA).
Blood collected in polyethylene tubes with heparin as an anticoagulant is hemolyzed. Lead is complexed with ammonium pyrrolidinedithiocarbamate (APDC) and the complex formed is extracted with methyl isobutyl ketone (MIBK). The lead contained in the organic phase is determined by flame Atomic Absorption Spectrophotometry, at a wavelength of 283.3 nm, using a direct quantification method. To determine analyte concentrations in a sample, the absorbances of standard solutions or standards of known analyte concentrations were first determined 12.
The value of these absorbances was then plotted against the concentrations, thus obtaining the calibration curve (concentration range from 0.1 to 10 µg/dL with an R2 of 0.99 to validate the straight line). Generally, analyte concentrations that have a linear relationship with absorbance are used, becoming known as the absorbance/concentration relationship “Calibration line”. Once the calibration line was established, the readings were taken and the concentration of the analyte was obtained 13.
The commercial brand Chroma™ was used, which is a lateral flow chromatography fluorescence immunoassay (FIA) for the quantitative determination of the level of Thyroid Stimulating Hormone (TSH), Free T3 and Free T4 in serum or plasma.
In order to adequately select participants, informed consent was obtained after explaining the objectives to the patients and volunteers. The research adhered to the criteria established in the fifth revision of the Declaration of Helsinki.
Metals, creatinine and thyroid profile were analyzed in triplicate. A descriptive statistical analysis was performed using measures of dispersion and central tendency, such as mean and standard deviation. Likewise, association and comparison tests(t-Student and Pearson correlation) were applied using the statistical program, Statistix10.0 for Windows.
In order to carry out the present investigation, 12 women and 8 men with an average age of 39 years with possible hyperthyroidism participated. The control group consisted of 20 people, 9 women and 11 men with an average age of 41 years, who met the parameters previously established in the research. In relation to the concentration of the hormones, a decrease in TSH and an increase in T3L were observed, being statistically significant with respect to the control for both hormones (Table 1).
With respect to the analysis of Pb in whole blood and Hg in partial urine, it was found that the study group presented values above the biological exposure index or permissible limit (BEIs) established by the American Conference of Governmental Industrial Hygienists Biological (ACGIH), 14, with Pb values up to 8 µg/dL for non-
| Metal | Estudy Group (M ± SD) | Control Group (M ± SD) | P |
|---|---|---|---|
| Pb | 11.4 ± 0.75 | 6.08 ± 0.18 | 0,012 * |
| Hg | 8.43 ± 0.11 | 3.92 ± 0.23 | 0,031 * |
When TSH and T3F levels were associated with Pb and Hg concentration, a significant negative association was observed for TSH (r=0.997 and r= 0.993), while for T3F there is a tendency to increase the levels of this hormone as the concentration of Pb Hg increases (r=0.997 and 0.976). The above is shown in Figures 1 a-b , 2a-b, 3a-b.


The Agency for Toxic Substances and Disease Registry (ATSDR), 15, indicates that there is evidence that certain heavy metals such as Pb and Hg can affect the endocrine system as an endocrine disruptor, affecting the physiological value of hormones and causing an endocrine imbalance. In the present study, it was shown that the free TSH, T3 hormones were outside the reference values, which is associated with what has been reported by various epidemiological studies that relate exposure to Pb and Hg with alteration of thyroid function, as well as alteration of cortisol and insulin levels 16,17. Previous publications include retrospective human studies that have correlated exposure to Pb, Hg and even Cd with alterations in thyroid hormone function, finding a positive correlation between blood and urine concentrations of these metals with all thyroid hormones, as well as thyroglobulin (Tg) 18. According to Kim et al. 1, Disrupted thyroid homeostasis plays a role in neurocognitive dysfunction and metabolic disorders. Since individuals are exposed to multiple metals simultaneously, it is important to assess the effects of metal mixtures on thyroid hormone status.
To understand what has been expressed above, it is essential to know that the toxic action of heavy metals in living organisms occurs through the blocking of biological activities, that is, enzymatic inactivation by the formation of bonds between the metal and sulfhydryl groups (-SH) and other functional groups of proteins and enzymes, causing irreversible damage in different organisms, displacing other metal ions or modifying the active conformation of biological molecules.
Vukelić et al.19, in their study, explored the influence of Pb on thyroid hormones and thyroid-related antibody levels in the rat model and revealed that low doses of Pb cause an increase in thyroid hormones (T4, FT4 and TSH) in rats after subacute exposure, while they had no impact on T3, T3F, anti-TPO and anti-Tg. Thus, they emphasize that the dose-dependent effects were the increase in T4 and T4F, where in addition, the in silico toxicogenomic data analysis showed that the main molecular pathways related to Pb-induced hyperthyroidism are connected to 14 genes. A study by Nie et al.20, which included 5,628 Chinese adults, showed the relationship of heavy metal levels in blood and serum antibodies against thyroid proteins and thyroid dysfunction reflected by total T3, total T4 and TSH levels.
Endocrine disruption has become a major human health problem, but it is difficult to study outside the laboratory for several reasons, including the multiplicity of exposures, the difficulty in assessing each exposure, and the variety of possible outcomes among human populations. In this regard, Castiello et al.21, examined the association of urinary concentrations of arsenic (As), cadmium (Cd), mercury (Hg), nickel (Ni), lead (Pb), manganese (Mn) and chromium (Cr) with blood pressure (BP) and serum hormone levels in male adolescents in Spain, showing significant associations between Hg and increased testosterone and luteinizing hormone (LH) and decreased thyroid-stimulating hormone (TSH); between the combination of As and Hg and increased LH and insulin-like growth factor 1; between Cr and decreased TSH; and between Cd and increased adrenocorticotropic hormone, concluding that these findings suggest that combined exposure to toxic metals, especially As and Cd, may contribute to elevated BP in male adolescents and that exposure to Hg, As, Cd and Cr may affect their hormone levels. Also considering that the world population is increasing and therefore more pregnancies, Gustin et al. 22, highlights that exposure to Cd and Hg, at levels globally prevalent through the diet, may affect thyroid function during pregnancy, independently of iodine and selenium levels. Further studies on potential implications for maternal and child health are warranted.Finally, a pilot study conducted by Nascimento et al. 23, investigated the possible association between exposure to these xenobiotics and thyroid dysfunction in children living in a rural community in southern Brazil, and found that elevated levels of these metals, along with higher levels of Pb and Hg, were associated with alterations in thyroid hormones.
Statistically significant differences were found in the average concentrations of TSH, T3F, lead and mercury in the study group. These results allow establishing a possible association of the aforementioned metals with hyperthyroidism, leaving then for the medical evaluation the definitive diagnosis and to consider within its profile the analysis of heavy metals.
Kim K, Argos M, Persky VW, Freels S, Sargis RM, Turyk ME. Associations of exposure to metal and metal mixtures with thyroid hormones Results from the NHANES 2007-2012. Environmental research. 2022;212(C):113413. DOI: 10.1016/j.envres.2022.113413 | |
Bhakat B, Pal J, Das S, Charaborty SK, SircarMedical NR, Kolkata RGK. A Prospective Study to Evaluate the Possible Role of Cholecalciferol Supplementation on Autoimmunity in Hashimoto's. Thyroiditis. 2023;71(1):1 | |
Durá-Travé T, Gallinas-Victoriano F. Autoimmune Thyroiditis and Vitamin D. International journal of molecular sciences,. 2024;25(6):3154. DOI: 10.3390/ijms25063154 | |
Alexander EK, Pearce EN, Brent GA, Brown RS, Chen H, Dosiou C, Grobman WA, Laurberg P, Lazarus JH, Mandel SJ, Peeters RP, Sullivan S. Guidelines of the American Thyroid Association for the Diagnosis and Management of Thyroid Disease During Pregnancy and the Postpartum. Thyroid. 2017;27(3):315–389. DOI: 10.1089/thy.2016.0457 | |
Korevaar TI. Based Tightrope Walking The 2017 Guidelines of the American Thyroid Association for the Diagnosis and Management of Thyroid Disease During Pregnancy and the Postpartum. Thyroid. 2017;27(3):309–311. DOI: 10.1089/thy.2017.29040.tko | |
Stagnaro-Green A. Clinical guidelines Thyroid and pregnancy - time for universal screening?. Nature reviews. Endocrinology. 2017;13(4):192–194. DOI: 10.1038/nrendo.2017.17 | |
Corona G, Croce L, Sparano C, Petrone L, Sforza A, Maggi M, Chiovato L, Rotondi M. Thyroid and heart, a clinically relevant relationship. J Endocrinol Invest. 2021;44(12):2535–2544. DOI: 10.1007/s40618-021-01590-9 | |
Tang J, Zhu Q, Xu Y, Zhou Y, Zhu L, Jin L, Wang W, Gao L, Chen G, Zhao H. Total arsenic, dimethylarsinic acid, lead, cadmium, total mercury, methylmercury and hypertension among Asian populations in the United States NHANES 2011-2018. Ecotoxicology and environmental safety. 2022;241:113776 | |
Desai G, Niu Z, Luo W, Frndak S, Shaver AL, Kordas K. Low-level exposure to lead, mercury, arsenic, and cadmium, and blood pressure among 8-17-year-old participants of the 2009-2016 National Health and Nutrition Examination Survey. Environmental research. 2021;197:111086. DOI: 10.1016/j.envres.2021.111086 | |
National Institute for Occupational Safety and Health Manual of analytical methods NMAM. Mercury: method 6009. (issue 2). 4th . p. 5. 1994 | |
Delanghe JR, Speeckaert MM. Creatinine determination according to. Jaffe-what does it stand for?. NDT plus. 2011;4(2):83–86. DOI: 10.1093/ndtplus/sfq211 | |
Frank JJ, Poulakos AG, Tornero-Velez R, Xue J. Systematic review and meta-analyses of lead (Pb) concentrations in environmental media (soil, dust, water, food, and air) reported in the United States from 1996 to 2016. The Science of the total environment,. 2019;694:133489. DOI: 10.1016/j.scitotenv.2019.07.295 | |
13. Martínez 2020. Martínez: Aplicación de la ley de Lambert-Beer en espectroscopia UV-visible; urihttps://m.riunet.uvp.es/handle/10251/16360https://m.riunet.uvp.es/handle/10251/16360 | |
American Conference of Governmental Industrial Hygienists Biological Exposure Indices (BIEs). 2015. Cincinnati, Ohio: ACGIH; urihttps://www.acgih.org/science/tlv-beiguidelines/biological-exposure-indices-beiintroduction/https://www.acgih.org/science/tlv-beiguidelines/biological-exposure-indices-beiintroduction/ | |
Agency for Toxic Substances and Disease Registry Resúmenes de Salud Pública - Benceno (Benzene). 2020. Atlanta: Division Of Toxicology and Environmental Medicine, ATSDR; | |
Javorac D, Andelkovic M, Repic A, Tatovic S, Djordjevic AB, Miljakovic EA, Batinic B, Boricic N, Ðukic-Cosic D, Antonijevic B, Bulat Z. Comprehensive insight into the neurotoxic mechanisms of low dose Pb exposure in Wistar rats Benchmark dose analysis. Chemico-biological interactions. 2022;360:109932. DOI: 10.1016/j.cbi.2022.109932 | |
Pacheco F, Florentino D, García J, Ali N. Alteraciones hematológicas y bioquímicas por exposición a benceno en trabajadores de, y cercanos a las estaciones de servicio. Salud de los trabajadores. 2023;31(2):179–191 | |
Chen A, Kim SS, Chung E, Dietrich KN. Thyroid hormones in relation to lead, mercury, and cadmium exposure in the National Health and Nutrition Examination Survey, 2007-2008. Environmental health perspectives. 2013;121(2):181–186. DOI: 10.1289/ehp.1205239 | |
Vukelic D, Djordjevic AB, Andelkovic M, Baralic K, Curcic M, Ðukic-Cosic D, Antonijevic B, Bulat Z. In vivo and in silico approach in revealing the influence of lead (Pb) on thyroid gland function. Environmental research,. 2023;237(2):117035. DOI: 10.1016/j.envres.2023.117035 | |
Nie X, Chen Y, Chen Y, Chen C, Han B, Li Q, Zhu C, Xia F, Zhai H, Wang N, Lu Y. Lead and cadmium exposure, higher thyroid antibodies and thyroid dysfunction in Chinese women. Environmental pollution. 2017;230:320–328. DOI: 10.1016/j.envpol.2017.06.052 | |
Castiello F, Olmedo P, Gil F, Molina M, Mundo A, Romero RR, Ruíz C, Gómez-Vida J, Vela-Soria F, Freire C. Association of urinary metal concentrations with blood pressure and serum hormones in Spanish male adolescents. Environmental Research. 2020;182:108958. DOI: 10.1016/j.envres.2019.108958 | |
Gustin K, Barman M, Skröder H, Jacobsson B, Sandin A, Sandberg AS, Wold AE, Vahter M, Kippler M. Thyroid hormones in relation to toxic metal exposure in pregnancy, and potential interactions with iodine and selenium. Environ Int. 2021;157:106869. DOI: 10.1016/j.envint.2021.106869 | |
Nascimento S, Göethel G, Gauer B, Sauer E, Nardi J, Cestonaro L, Correia D, Peruzzi C, Mota L, Machry RV, Furlanetto TW, Saint' Pierre T, Gioda A, Arbo MD, Garcia SC. Exposure to environment chemicals and its possible role in endocrine disruption of children from a rural area. Environmental research. 2018;167:488–498. DOI: 10.1016/j.envres.2018.07.039 |