Hostname: page-component-586b7cd67f-rdxmf Total loading time: 0 Render date: 2024-11-26T14:13:58.399Z Has data issue: false hasContentIssue false

Measuring iodine status in diverse populations

Published online by Cambridge University Press:  31 July 2015

Kevin A. Cockell*
Affiliation:
Nutrition Research Division, Food Directorate, Health Canada, 2203E Banting Research Centre, 251 Sir Frederick Banting Driveway, Ottawa, ON, CanadaK1A [email protected]
Rights & Permissions [Opens in a new window]

Abstract

Type
Invited Commentary
Copyright
Copyright © Her Majesty the Queen in Right of Canada, as represented by the Minister of Health (2015). 

Measurement of iodine status is one of those things that can seem simple until you get into the details. The recent paper by Andersen et al. ( Reference Andersen, Waagepetersen and Laurberg 1 ) in the British Journal of Nutrition provides some important new insights into, and an opportunity to reflect on, some fundamental considerations.

Iodine is an essential nutrient through its role in thyroid hormones, and must be obtained from the diet in sufficient, but not excessive, amounts( Reference Rohner, Zimmermann and Jooste 2 ). Iodine deficiency is a global public health issue( 3 ) and although progress has been made, there is continuing concern( Reference Andersson, Karumbunathan and Zimmermann 4 ) so that it remains necessary to monitor iodine status in diverse populations. Excessive iodine consumption may be a more localised than widespread phenomenon, as relatively few food groups are rich in iodine( Reference Rasmussen, Andersen, Ovesen, Preedy, Burrow and Watson 5 ), although some areas with high iodine content of drinking water, for example, also cause concern about high iodine exposures( Reference Lv, Xu and Wang 6 ). Some subpopulations, such as those with autoimmune thyroiditis, may be more sensitive to excess iodine(7).

Urinary iodine excretion (UIE) is commonly used as a population biomarker to assess recent iodine exposure or iodine status across the spectrum from deficiency to excess( Reference Rohner, Zimmermann and Jooste 2 ), as typically more than 90 % of ingested iodine appears in urine within 24–48 h( Reference Nath, Moinier and Thuillier 8 ). The concentration of iodine is ideally measured on a 24-h urine sample, though practicalities (including concerns of compliance with 24-h sampling) or study logistics (such as large field surveys) may dictate the use of a timed interval other than 24 h or, more often, a convenient ‘spot’ urine sample.

A single measurement of a spot or 24-h urine sample cannot provide reliable information about the iodine status of an individual, due to high intra-individual variation( Reference Andersen, Pedersen and Pedersen 9 ). The population median of measurements on spot or 24-h samples from a sufficiently large group, say 50–100 or more( Reference Zimmermann and Andersson 10 Reference Vejberg, Knudsen and Perrild 12 ) can be used as an index of the overall iodine status of the group; this is what is suitable for comparison with established population thresholds( 3 ). Newer methodologies involve two independent urine iodine measurements per participant for a sufficient subsample of the study population. When followed by appropriate statistical procedures to eliminate intra-individual variation, population distribution curves of usual iodine intake or excretion can be obtained; these are suitable for evaluation of the proportion of the population with deficient or excessive intakes( Reference Rohner, Zimmermann and Jooste 2 , Reference Zimmermann and Andersson 10 ). In contrast, traditional methodologies require as many as ten or twelve independent measures per individual in order to determine an individual's iodine status even within 20 % precision( Reference Andersen, Karmisholt and Pedersen 13 , Reference König, Andersson and Hotz 14 ).

The result of urinary iodine excretion measurement is commonly expressed as 24-h UIE (μg/24 h or μg/d) in the case of 24-h collection. In the case of analysis of spot urine samples the result is expressed in terms of urinary iodine concentration (UIC, μg/l). In some instances, the UIC is adjusted for measured urinary creatinine concentration (creatinine-adjusted UIC, or UICC, μg/g creatinine). Creatinine-adjusted values can further be extrapolated to an estimate of 24-h UIE (eUIE, μg/24 h) based on the expected level of creatinine excretion for a 24-h period, since creatinine production from body creatine pools is relatively constant( Reference Barr, Wilder and Caudill 15 ). These different ways of expressing urine iodine are sometimes treated interchangeably, as reflected by the statement in the present Andersen et al. ( Reference Andersen, Waagepetersen and Laurberg 1 ) paper: ‘The different measures of iodine in urine were compared as they are all used to portray the iodine nutrition by the same unit (μg)’; but the units are indeed different. This generalisation may be more reasonable when the study focuses on school-aged children, whose daily urine volume approximates 1 litre. But it does not apply well to adults whose daily urine volume is usually larger. Andersen et al. ( Reference Andersen, Waagepetersen and Laurberg 1 ) go on to demonstrate clearly that the population median iodine values can also be quite different, when the four measures UIE, UIC, UICC and eUIE are all determined within one study.

Creatinine adjustment has fallen out of favour for global comparisons, although it is intended to account for differences in hydration level of the participants of research studies. This because the expected creatinine excretion can be much lower in cases of protein malnutrition( Reference Zimmermann and Andersson 10 ). In a population sample large enough, differences in hydration are considered to cancel out, so that the population median UIC is adequately representative of the group. Excluding severe malnutrition, other factors such as age, sex (or more specifically muscle mass) and even diets high in red meat are known to influence creatinine excretion( Reference Barr, Wilder and Caudill 15 ). Creatinine adjustment of UIC, referred to previously, can involve the use of age- and sex-specific estimates of 24-h urine creatinine excretion to yield eUIE (μg/24 h)( Reference Knudsen, Christiansen and Brandt-Christiansen 16 ). Andersen et al. ( Reference Andersen, Waagepetersen and Laurberg 1 ) in their present paper have extended this principle to include age-, sex-, and ethnic-specific creatinine adjustment, having recently established that Inuit v. non-Inuit study participants in Greenland differed significantly in their creatinine excretion( Reference Andersen, Dehnfeld and Laurberg 17 ). Thus, in the context of a specific study such as their investigations on Greenland populations( Reference Andersen, Waagepetersen and Laurberg 1 ), creatinine adjustment can provide advantages that outweigh the burden of additional analyses.

Andersen et al. ( Reference Andersen, Waagepetersen and Laurberg 1 ) identified differences in iodine excretion between Inuit and non-Inuit in the present study, and noted that the ethnicity influence was accounted for by differences in diet. This differs somewhat from the conclusions of their recent work on vitamin D status in this population, where they documented a diet–ethnicity interaction( Reference Andersen, Laurberg and Hvingel 18 ), but still speak of an important effect of dietary changes on nutritional status in a society in transition, which they had first documented for iodine a decade ago( Reference Andersen, Hvingel and Kleinschmidt 19 ).

The key conclusion of the present work by Andersen et al. ( Reference Andersen, Waagepetersen and Laurberg 1 ) is that the relationship between spot v. 24-h urine sampling as biomarkers for iodine status is not necessarily the same across the spectrum from deficiency to excess. They highlight this as a risk for misinterpretation of iodine status, depending upon the biomarker being used, particularly at higher levels of iodine excretion. This is a useful concept, as it expands on the considerations for selection and interpretation of appropriate biomarkers; it reinforces the need for validation of a biomarker for the specific purpose to which it is being applied in investigational or surveillance contexts. The Biomarkers of Nutrition for Development project is set to document these kinds of considerations for nutrients of high public health importance, including iodine( Reference Rohner, Zimmermann and Jooste 2 ). Careful and appropriate selection of biomarkers will better address the questions asked in research and in population monitoring.

References

1 Andersen, S, Waagepetersen, R & Laurberg, P (2015) Misclassification of iodine intake level from morning spot urine samples with high iodine excretion among Inuit and non-Inuit in Greenland. Br J Nutr 113, 14331440.Google Scholar
2 Rohner, F, Zimmermann, M, Jooste, P, et al. (2014) Biomarkers of nutrition for development – iodine review. J Nutr 144, 1322S1342S.Google Scholar
3 World Health Organization (2007) Assessment of Iodine Deficiency Disorders and Monitoring Their Elimination: A Guide for Programme Managers, 3rd ed. Geneva: WHO (WHO/UNICEF/ICCIDD).Google Scholar
4 Andersson, M, Karumbunathan, V & Zimmermann, MB (2012) Global iodine status in 2011 and trends over the past decade. J Nutr 142, 744750.CrossRefGoogle ScholarPubMed
5 Rasmussen, LB, Andersen, A, Ovesen, L, et al. (2009) Iodine intake and food choice. In Comprehensive Handbook of Iodine: Nutritional, Biochemical, Pathological and Therapeutic Aspects, chapter 35, pp. 333338 [Preedy, VR, Burrow, GN and Watson, RR, editors]. New York, NY: Academic Press.Google Scholar
6 Lv, S, Xu, D, Wang, Y, et al. (2015) Impact of removing iodised salt on children's goitre status in areas with excessive iodine in drinking-water. Br J Nutr 113, 114119.Google Scholar
7 Institute of Medicine (2001) Iodine. In Dietary Reference Intakes for Vitamin A, Vitamin K, Arsenic, Boron, Chromium, Copper, Iodine, Iron, Manganese, Molybdenum, Nickel, Silicon, Vanadium, and Zinc, chapter 8, pp. 258289. Washington, DC: National Academy of Sciences, National Academy Press.Google Scholar
8 Nath, SK, Moinier, B, Thuillier, F, et al. (1992) Urinary excretion of iodide and fluoride from supplemented food grade salt. Int J Vitam Nutr Res 62, 6672.Google Scholar
9 Andersen, S, Pedersen, KM, Pedersen, IB, et al. (2001) Variations in urinary iodine excretion and thyroid function. A 1-year study in healthy men. Eur J Endocrinol 144, 461465.Google Scholar
10 Zimmermann, MB & Andersson, M (2012) Assessment of iodine nutrition in populations: past, present and future. Nutr Rev 70, 553570.Google Scholar
11 Karmisholt, J, Laurberg, P & Andersen, S (2014) Recommended number of participants in iodine nutrition studies is similar before and after an iodine fortification programme. Eur J Nutr 53, 487492.CrossRefGoogle ScholarPubMed
12 Vejberg, P, Knudsen, N, Perrild, H, et al. (2009) Estimation of iodine intake from various urinary iodine measurements in population studies. Thyroid 19, 12811286.Google Scholar
13 Andersen, S, Karmisholt, J, Pedersen, KM, et al. (2008) Reliability of studies of iodine intake and recommendations for number of samples in groups and in individuals. Br J Nutr 99, 813818.Google Scholar
14 König, F, Andersson, M, Hotz, K, et al. (2011) Ten repeat collections for urinary iodine from spot samples or 24-hour samples are needed to reliably estimate individual iodine status in women. J Nutr 141, 20492054.Google Scholar
15 Barr, DB, Wilder, LC, Caudill, SP, et al. (2005) Urinary creatinine concentrations in the U.S. population: implications for urinary biologic monitoring measurements. Environ Health Perspect 113, 192200.Google Scholar
16 Knudsen, N, Christiansen, E, Brandt-Christiansen, M, et al. (2000) Age-and sex-adjusted iodine/creatinine ratio. A new standard in epidemiological surveys? Evaluation of three different estimates of iodine excretion based on casual urine samples and comparison to 24 h values. Eur J Clin Nutr 54, 361363.Google Scholar
17 Andersen, S, Dehnfeld, M & Laurberg, P (2015) Ethnicity is important for creatinine excretion among Inuit and Caucasians in Greenland. Scand J Clin Lab Invest 75, 4450.Google Scholar
18 Andersen, S, Laurberg, P, Hvingel, B, et al. (2013) Vitamin D status in Greenland is influenced by diet and ethnicity: a population-based survey in an Arctic society in transition. Br J Nutr 109, 928935.Google Scholar
19 Andersen, S, Hvingel, B, Kleinschmidt, K, et al. (2005) Changes in iodine excretion in 50–60-y-old denizens of an Arctic society in transition and iodine excretion as a biomarker of the frequency of consumption of traditional Inuit foods. Am J Clin Nutr 81, 656663.CrossRefGoogle ScholarPubMed