Abstract
Background
5-chloro-2-(2,4-dichlorophenoxy)phenol (triclosan) is used as an antiseptic and is a potential endocrine-disrupting chemical that can affect thyroid hormone levels. This study evaluated the relationship between triclosan exposure and thyroid hormones.
Methods
Data from the second Korean National Environmental Health Survey (2012–2014) were analyzed. Triclosan exposure was evaluated using urinary triclosan concentrations and classified into 2 groups: ‘below detection (< limit of detection [LOD])' vs. ‘detected (≥ LOD).' Multiple linear regression analysis was conducted to determine the relationship between triclosan exposure and the serum thyroid hormone concentrations, adjusting for age, body mass index, urinary creatinine, and smoking status.
Results
When grouped by sex, triclosan exposure was positively associated with the serum thyroid-stimulating hormone (TSH) concentrations in females with marginal significance (β = 0.066, p = 0.058). However, no significant association was identified between triclosan exposure and serum total triiodothyronine and thyroxine in both males and females, and TSH in males.
Conclusions
This study is the first human study to evaluate the relationship between triclosan exposure and serum thyroid hormone concentrations in the Korean population. There was suggestive positive association between triclosan exposure and the serum TSH in females. Further studies need to evaluate the relationship between long-term exposure to low-dose triclosan and thyroid hormones.
References
1. Dann AB, Hontela A. Triclosan: environmental exposure, toxicity and mechanisms of action. J Appl Toxicol. 2011; 31(4):285–311.
2. Lu S, Yu Y, Ren L, Zhang X, Liu G, Yu Y. Estimation of intake and uptake of bisphenols and triclosan from personal care products by dermal contact. Sci Total Environ. 2018; 621:1389–96.
3. Singer H, Müller S, Tixier C, Pillonel L. Triclosan: occurrence and fate of a widely used biocide in the aquatic environment: field measurements in wastewater treatment plants, surface waters, and lake sediments. Environ Sci Technol. 2002; 36(23):4998–5004.
4. Rodricks JV, Swenberg JA, Borzelleca JF, Maronpot RR, Shipp AM. Triclosan: a critical review of the experimental data and development of margins of safety for consumer products. Crit Rev Toxicol. 2010; 40(5):422–84.
5. Krishnan K, Gagné M, Nong A, Aylward LL, Hays SM. Biomonitoring equivalents for triclosan. Regul Toxicol Pharmacol. 2010; 58(1):10–7.
6. Sandborgh-Englund G, Adolfsson-Erici M, Odham G, Ekstrand J. Pharmacokinetics of triclosan following oral ingestion in humans. J Toxicol Environ Health A. 2006; 69(20):1861–73.
7. Robertshaw H, Leppard B. Contact dermatitis to triclosan in toothpaste. Contact Dermat. 2007; 57(6):383–4.
8. Savage JH, Matsui EC, Wood RA, Keet CA. Urinary levels of triclosan and parabens are associated with aeroallergen and food sensitization. J Allergy Clin Immunol. 2012; 130(2):453–460. e7.
9. Stoker TE, Gibson EK, Zorrilla LM. Triclosan exposure modulates estrogen-dependent responses in the female Wistar rat. Toxicol Sci. 2010; 117(1):45–53.
10. Kumar V, Chakraborty A, Kural MR, Roy P. Alteration of testicular steroidogenesis and histopathology of reproductive system in male rats treated with triclosan. Reprod Toxicol. 2009; 27(2):177–85.
11. Zorrilla LM, Gibson EK, Jeffay SC, Crofton KM, Setzer WR, Cooper RL, et al. The effects of triclosan on puberty and thyroid hormones in male Wistar rats. Toxicol Sci. 2009; 107(1):56–64.
12. Koeppe ES, Ferguson KK, Colacino JA, Meeker JD. Relationship between urinary triclosan and paraben concentrations and serum thyroid measures in NHANES 2007–2008. Sci Total Environ. 2013; 445–446:299–305.
13. Johnson PI, Koustas E, Vesterinen HM, Sutton P, Atchley DS, Kim AN, et al. Application of the navigation guide systematic review methodology to the evidence for developmental and reproductive toxicity of triclosan. Environ Int. 2016; 92–93:716–28.
14. Etzel TM, Calafat AM, Ye X, Chen A, Lanphear BP, Savitz DA, et al. Urinary triclosan concentrations during pregnancy and birth outcomes. Environ Res. 2017; 156:505–11.
15. Allmyr M, Panagiotidis G, Sparve E, Diczfalusy U, Sandborgh-Englund G. Human exposure to triclosan via toothpaste does not change CYP3A4 activity or plasma concentrations of thyroid hormones. Basic Clin Pharmacol Toxicol. 2009; 105(5):339–44.
16. Crofton KM, Paul KB, Devito MJ, Hedge JM. Short-term in vivo exposure to the water contaminant triclosan: evidence for disruption of thyroxine. Environ Toxicol Pharmacol. 2007; 24(2):194–7.
17. Paul KB, Hedge JM, DeVito MJ, Crofton KM. Short-term exposure to triclosan decreases thyroxine in vivo via upregulation of hepatic catabolism in young long-evans rats. Toxicol Sci. 2010; 113(2):367–79.
18. Axelstad M, Boberg J, Vinggaard AM, Christiansen S, Hass U. Triclosan exposure reduces thyroxine levels in pregnant and lactating rat dams and in directly exposed offspring. Food Chem Toxicol. 2013; 59:534–40.
19. Geens T, Dirtu AC, Dirinck E, Malarvannan G, Van Gaal L, Jorens PG, et al. Daily intake of bisphenol A and triclosan and their association with anthropometric data, thyroid hormones and weight loss in overweight and obese individuals. Environ Int. 2015; 76:98–105.
20. Wang X, Ouyang F, Feng L, Wang X, Liu Z, Zhang J. Maternal urinary triclosan concentration in relation to maternal and neonatal thyroid hormone levels: a prospective study. Environ Health Perspect. 2017; 125(6):067017.
21. Cullinan MP, Palmer JE, Carle AD, West MJ, Seymour GJ. Long term use of triclosan toothpaste and thyroid function. Sci Total Environ. 2012; 416:75–9.
22. Ley C, Pischel L, Parsonnet J. Triclosan and triclocarban exposure and thyroid function during pregnancy-a randomized intervention. Reprod Toxicol. 2017; 74:143–9.
23. Paul KB, Hedge JM, Bansal R, Zoeller RT, Peter R, DeVito MJ, et al. Developmental triclosan exposure decreases maternal, fetal, and early neonatal thyroxine: a dynamic and kinetic evaluation of a putative mode-of-action. Toxicology. 2012; 300(1–2):31–45.
24. Butt CM, Stapleton HM. Inhibition of thyroid hormone sulfotransferase activity by brominated flame retardants and halogenated phenolics. Chem Res Toxicol. 2013; 26(11):1692–702.
25. Butt CM, Wang D, Stapleton HM. Halogenated phenolic contaminants inhibit the in vitro activity of the thyroid-regulating deiodinases in human liver. Toxicol Sci. 2011; 124(2):339–47.
26. Shimizu R, Yamaguchi M, Uramaru N, Kuroki H, Ohta S, Kitamura S, et al. Structure-activity relationships of 44 halogenated compounds for iodotyrosine deiodinase-inhibitory activity. Toxicology. 2013; 314(1):22–9.
27. Skarha J, Mínguez-Alarcón L, Williams PL, Korevaar TIM, de Poortere RA, Broeren MAC, et al. Cross-sectional associations between urinary triclosan and serum thyroid function biomarker concentrations in women. Environ Int. 2019; 122:256–62.
28. Aker AM, Johns L, McElrath TF, Cantonwine DE, Mukherjee B, Meeker JD. Associations between maternal phenol and paraben urinary biomarkers and maternal hormones during pregnancy: a repeated measures study. Environ Int. 2018; 113:341–9.
29. Apel P, Angerer J, Wilhelm M, Kolossa-Gehring M. New HBM values for emerging substances, inventory of reference and HBM values in force, and working principles of the German human biomonitoring commission. Int J Hyg Environ Health. 2017; 220(2 Pt A):152–66.
30. Calafat AM, Ye X, Wong LY, Reidy JA, Needham LL. Urinary concentrations of triclosan in the U.S. population: 2003–2004. Environ Health Perspect. 2008; 116(3):303–7.
Table 1.
Table 2.
Variable | Category | No. (weighted %) | Total T3 (ng/dL) | Total T4 (µg/dL) | TSH (µIU/mL) | Triclosan detected* | |||
---|---|---|---|---|---|---|---|---|---|
Unweighted GM (95% CI) | Weighted GM (95% CI) | Unweighted GM (95% CI) | Weighted GM (95% CI) | Unweighted GM (95% CI) | Weighted GM (95% CI) | No. (weighted %) | |||
Sex | Male | 2,630 (50.3) | 101.63 (100.93–102.32) | 102.08 (100.91–103.28) | 7.93 (7.88–7.99) | 7.96 (7.88–8.04) | 1.81 (1.76–1.85) | 1.77 (1.72–1.82) | 1,010 (41.5) |
Female | 3,360 (49.7) | 96.22 (95.65–96.79) | 95.62 (94.60–96.64) | 7.96 (7.91–8.01) | 7.96 (7.88–8.04) | 2.03 (1.98–2.07) | 1.96 (1.91–2.02) | 1,409 (43.9) | |
p-value | < 0.001 | < 0.001 | 0.534 | 0.991 | < 0.001 | < 0.001 | 0.158 | ||
Age | 19–29 | 499 (17.7) | 98.36 (96.88–99.84)‡ | 98.35 (96.38–100.35) | 8.01 (7.88–8.15) | 7.98 (7.82–8.14) | 1.53 (1.46–1.62)† | 1.53 (1.45–1.62)† | 255 (49.4) |
(years) | 30–39 | 981 (20.0) | 98.06 (96.95–99.19)‡ | 99.13 (97.43–100.87) | 7.93 (7.84–8.01) | 7.97 (7.85–8.09) | 1.82 (1.75–1.88)‡ | 1.77 (1.69–1.85)‡ | 422 (43.8) |
40–49 | 1,153 (21.5) | 98.47 (97.50–99.46)‡ | 98.35 (96.71–100.00) | 7.94 (7.86–8.02) | 7.96 (7.84–8.07) | 1.97 (1.90–2.04)§ | 1.94 (1.86–2.02)§ | 508 (45.1) | |
50–59 | 1,325 (19.3) | 99.49 (98.53–100.47)‡ | 100.33 (98.95–101.74) | 7.90 (7.82–7.98) | 7.92 (7.81–8.03) | 2.04 (1.97–2.12)§ | 2.03 (1.93–2.13)§ | 549 (42.9) | |
60–69 | 1,232 (11.0) | 99.67 (98.67–100.69)‡ | 98.98 (97.43–100.55) | 7.99 (7.90–8.08) | 7.95 (7.83–8.07) | 2.00 (1.93–2.08)§ | 2.05 (1.95–2.15)§ | 435 (35.5) | |
≥ 70 | 800 (10.4) | 96.14 (94.94–97.36)† | 97.03 (95.28–98.81) | 7.94 (7.83–8.04) | 7.98 (7.84–8.12) | 1.98 (1.88–2.08)§ | 2.05 (1.92–2.18)§ | 250 (31.6) | |
p-value | < 0.001 | 0.073 | 0.629 | 0.985 | < 0.001 | < 0.001 | < 0.001 | ||
p for trend | 0.331 | 0.794 | 0.616 | 0.766 | < 0.001 | < 0.001 | |||
BMI | < 18.50 | 142 (3.0) | 93.51 (90.41–96.72)† | 93.07 (89.26–97.04)† | 8.01 (7.75–8.28) | 8.19 (7.88–8.51) | 1.58 (1.42–1.75)† | 1.44 (1.26–1.63)† | 58 (40.9) |
(kg/m2) | 18.50–22.99 | 2,040 (36.4) | 95.51 (94.77–96.24)† | 95.71 (94.57–96.85)† | 7.95 (7.89–8.01) | 7.93 (7.83–8.02) | 1.84 (1.79–1.90)‡ | 1.80 (1.74–1.86)‡ | 832 (42.4) |
23.00–24.99 | 1,491 (23.1) | 98.67 (97.81–99.53)‡ | 99.08 (97.72–100.45)‡ | 7.89 (7.82–7.97) | 7.90 (7.79–8.01) | 1.96 (1.90–2.03)‡ | 1.86 (1.79–1.93)‡ | 606 (43.3) | |
≥ 25.00 | 2,317 (37.5) | 101.57 (100.83–102.31)§ | 102.26 (101.00–103.53)§ | 7.97 (7.91–8.03) | 8.01 (7.92–8.10) | 2.00 (1.95–2.06)‡ | 1.97 (1.91–2.04)§ | 923 (42.8) | |
p-value | < 0.001 | < 0.001 | 0.403 | 0.088 | < 0.001 | < 0.001 | 0.962 | ||
p for trend | < 0.001 | < 0.001 | 0.656 | 0.480 | < 0.001 | < 0.001 | |||
Smoking | Smoker | 1,090 (22.0) | 104.19 (103.06–105.33) | 104.57 (102.87–106.31) | 8.09 (8.00–8.18) | 8.10 (7.98–8.21) | 1.60 (1.54–1.65) | 1.60 (1.53–1.67) | 408 (40.7) |
status | Current non-smoker | 4,900 (78.0) | 97.34 (96.86–97.82) | 97.25 (96.27–98.23) | 7.91 (7.87–7.95) | 7.92 (7.84–7.99) | 2.01 (1.97–2.05) | 1.95 (1.90–1.99) | 2,011 (43.3) |
p-value | < 0.001 | < 0.001 | < 0.001 | 0.003 | < 0.001 | < 0.001 | 0.230 | ||
Total | 5,990 (100) | 98.55 (98.11–99.00) | 98.82 (97.83–99.81) | 7.95 (7.91–7.98) | 7.96 (7.89–8.03) | 1.93 (1.89–1.96) | 1.86 (1.83–1.90) | 2,419 (42.7) |
BMI: body mass index; T3: triiodothyronine; T4: thyroxine; TSH: thyroid-stimulating hormone; Triclosan: 5-chloro-2-(2,4-dichlorophenoxy)phenol; GM: geometric mean; CI: confidence interval; LOD: limit of detection.
Table 3.
Triclosan exposure group | ln total T3 (ng/dL) | Total T3 (ng/dL) | ln total T4 (µg/dL) | Total T4 (µg/dL) | ln TSH (µIU/mL) | TSH (µIU/mL) |
---|---|---|---|---|---|---|
β (95% CI) | Estimated mean (95% CI) | β (95% CI) | Estimated mean (95% CI) | β (95% CI) | Estimated mean (95% CI) | |
Male | ||||||
Detected (≥ LOD‡) | 0.000 (−0.019, 0.018) | 103.11 (101.36, 104.88) | −0.011 (−0.033, 0.010) | 7.95 (7.82, 8.08) | 0.028 (−0.035, 0.091) | 1.76 (1.68, 1.85) |
Below detection (< LO | OD) 0 (reference) | 103.13 (101.85, 104.43) | 0 (reference) | 8.04 (7.94, 8.15) | 0 (reference) | 1.71 (1.65, 1.78) |
p-value | 0.984 | 0.298 | 0.379 | |||
Female | ||||||
Detected (≥ LOD) | −0.010 (−0.028, 0.007) | 94.79 (92.02, 97.64) | −0.010 (−0.028, 0.008) | 7.93 (7.70, 8.16) | 0.066 (−0.002, 0.134) | 1.86 (1.71, 2.02) |
Below detection (< LO | OD) 0 (reference) | 95.78 (92.82, 98.84) | 0 (reference) | 8.01 (7.80, 8.22) | 0 (reference) | 1.74 (1.60, 1.89) |
p-value | 0.251 | 0.288 | 0.058 |
T3: triiodothyronine; T4: thyroxine; TSH: thyroid-stimulating hormone; Triclosan: 5-chloro-2-(2,4-dichlorophenoxy)phenol; CI: confidence interval; LOD: limit of detection.