Diabetes: Original Article
Marine Food Pollutants as a Risk Factor for Hypoinsulinemia and Type 2 Diabetes
Grandjean, Philippea,b; Henriksen, Jan Erikc; Choi, Anna L.b; Petersen, Maria Skaalumd; Dalgård, Christinea; Nielsen, Flemminga; Weihe, Pald
From the aInstitute of Public Health, University of Southern Denmark, Odense, Denmark; bDepartment of Environmental Health, Harvard School of Public Health, Boston, MA; cDepartment of Endocrinology, Odense University Hospital, Odense, Denmark; and dFaroese Hospital System, Torshavn, Faroe Islands.
Submitted 26 March 2010; accepted 26 November 2010; posted 1 March 2011.
Supported by a grant from the National Institute of Health (ES013692) and the European Commission Sixth Framework Programme for RTD (FOOD-CT-2006-016253, PHIME).
Correspondence: Philippe Grandjean, Harvard School of Public Health, 401 Park Drive, Room 3-110, Landmark Center, East, PO Box 15967, Boston, MA 02215. E-mail: email@example.com.
Background: Some persistent environmental chemicals are suspected of causing an increased risk of type 2 diabetes mellitus, a disease particularly common after the age of 70. This concern was examined in a cross-sectional study of elderly subjects from a fishing population with elevated contaminant exposures from seafood species high in the food chain.
Methods: Clinical examinations of 713 Faroese residents aged 70–74 years (64% of eligible population) included fasting plasma concentrations of glucose and insulin, and glycosylated hemoglobin. Lifetime exposure to persistent environmental chemicals from pilot whale and other traditional food was estimated from a dietary questionnaire and by analysis of blood samples for polychlorinated biphenyls (PCBs) and related food contaminants.
Results: Septuagenarians with type 2 diabetes or impaired fasting glycemia tended to have higher PCB concentrations and higher past intake of traditional foods, especially during childhood and adolescence. In nondiabetic subjects, the fasting insulin concentration decreased by 7% (95% CI = −12% to −2%) for each doubling of the PCB concentration after adjustment for sex and body mass index at age 20. Conversely, the fasting glucose concentration increased by 6% (−1% to 13%) for each doubling in PCB. Similar associations were seen in subjects without impaired fasting glycemia, while further adjustment for current body mass index and lipid metabolism parameters attenuated some of the associations.
Conclusions: Impaired insulin secretion appears to constitute an important part of the type 2 diabetes pathogenesis associated with exposure to persistent lipophilic food contaminants.
The increasing prevalence of type 2 diabetes mellitus has been linked primarily to obesity and lack of exercise.1 Experimental evidence suggests that exposure to dioxins and other persistent halogenated chemicals may result in both insulin resistance and disruption of insulin secretion.2 Epidemiologic studies also support a role for environmental chemicals in the etiology of type 2 diabetes. Thus, in subjects with high-level exposure to dioxins and related substances, an increased risk of developing diabetes has been documented, in some cases more clearly in women.3–5 Within the general population, diabetes patients have higher serum concentrations of persistent, lipophilic pollutants, including polychlorinated biphenyls (PCBs) and the pesticide metabolite 2,2-bis(4-chlorophenyl)-1,1-dichloroethene (DDE).6–11 In addition, subjects with impaired fasting glycemia also tend to have higher cumulated pollutant concentrations in serum.12,13 Adult Greenland Inuit showed an inverse relation between the serum PCB concentration and the insulin concentration at 2 hours after glucose challenge.14 Likewise, in US veterans with existing diabetes, fasting insulin concentrations decreased at higher exposures.15 However, nondiabetic veterans at an average age of 53 years showed higher fasting serum-insulin concentrations at increased dioxin exposure levels.9
The pathogenesis of type 2 diabetes may originate decades before the clinical diagnosis is made.16 Thus, some general population studies have analyzed banked serum samples obtained before the appearance of clinical abnormalities.9,17 However, given that the elimination half-time may be as long as 10 years for dioxins, certain PCB congeners, and DDE,18 concurrent serum concentrations may provide a reasonable estimate of cumulated past exposures. However, these lipophilic pollutants accumulate in fat tissue. Subjects with a high body mass index (BMI) therefore dilute their body burden within a larger distribution volume, while storage in body fat on the other hand leads to a longer retention of the chemicals.19 Even so, the elimination half-life does not seem to be affected by the development of type 2 diabetes.20 In addition, the known BMI-associated increase in diabetes risk has been found to be greater in subjects with an increased serum concentration of the pollutants,8 thus calling for assessment of possible interactions.
In searching for clues to shed new light on the possible etiologic role of lipophilic pollutants, we have examined abnormalities of glucose metabolism in Faroese elderly residents with a high risk of diabetes development. The Faroe Islands community offers a unique research opportunity, as pollutant exposures primarily originate from traditional diets that include seabirds and blubber of the pilot whale. Past exposures may therefore be assessed by dietary questionnaire as well as by serum analysis.
Study Design and Subjects
A cohort of 1131 residents of the Faroe Islands aged 70–74 years was formed based on information obtained from the residents' registry. The Faroese reside on a dozen islands in the Northern Atlantic between Norway and Iceland; about 80% live on 4 northern islands connected by tunnel or bridge. Access to the examination clinic at the National Hospital in Tórshavn is therefore rather easy for most subjects. Transportation costs were reimbursed. The oldest subjects were invited first for the examinations, which took place over a 12-month period. A total of 713 subjects were examined (64% of the eligible population, excluding 14 deceased).21 Birthweights were extracted from the midwife charts kept at the Faroese National Archives.
A maximum of 6 septuagenarians per day arrived at the clinic before breakfast and, as the first procedure, fasting blood samples were obtained. All subjects then underwent a thorough physical examination that included measurement of body weight and height.
A capillary blood sample was used to determine the glucose concentration, using the Precision Xceed instrument from MediSense and the Abbott Precision Xtra Plus strips. The blood value was automatically transformed to the fasting plasma glucose concentration by multiplying by 1.12. A fasting whole blood sample obtained by venipuncture was used to determine the relative concentration of glycosylated hemoglobin (HbA1c) by high-pressure liquid chromatography. Plasma was used for determination of the fasting insulin concentration by time-resolved fluoroimmunoassay (AutoDelfia, PerkinElmer Life and Analytical Sciences, Walla Oy, Turku, Finland). Serum total cholesterol and triglycerides were measured by an enzymatic reaction (Modular P, Roche Diagnostics Ltd). The analytic imprecision of these assays was <5%.
Subjects not previously diagnosed with type 2 diabetes mellitus were considered incident (new) cases if the fasting plasma glucose exceeded 6.9 mmol/L or if the HbA1c exceeded 6.4%. Further, subjects were classified as having impaired fasting glycemia if their fasting plasma glucose was between 6.1 and 6.9 mmol/L.22 Insulin resistance was estimated by the homeostasis model assessment from fasting plasma insulin (FPI) and fasting plasma glucose (FPG) concentrations as FPI × FPG/22.5, whereas the beta cell function was expressed as the beta index of (20 × FPI)/(FPG × 3.5).22
Cumulated exposures to major marine contaminants were assessed from analysis of blood samples. Serum was analyzed for persistent organochlorine pollutants by gas chromatography using a dual-capillary column system with microelectron capture detection after solid phase extraction.23 To avoid problems with congeners not assessed and concentrations below the detection limit, a simplified total PCB concentration was calculated as the sum of congeners CB-138, CB-153, and CB-180 multiplied by 2.23 This analysis also provided the concentrations of DDE. Other environmental chemicals were also detected, but because of their much lower concentrations and their close correlations with PCB and DDE, these additional analytes were not examined further. As the organochlorine substances are lipophilic, PCB and DDE concentrations were expressed in relation to the total lipid concentration in the serum, as determined by a kit from Cypress Diagnostics (Langdorp, Belgium). For comparison, we also measured the blood-mercury concentration by atomic absorption as a known indicator of recent seafood intake.24
Current health and past medical history, including medication, were recorded by structured interview. A dietary questionnaire was used to ascertain the intake of traditional and other food during childhood and adolescence, adulthood, and the most recent year. The questionnaire focused on the amount of local food items, such as fish, whale meat and blubber, and seabirds in the diet.25 Other risk factors of possible relevance (such as smoking and alcohol use, and body weight at age 20) were also recorded.
The study protocol was approved by the ethical review committee serving the Faroe Islands and by the Institutional Review Board at Harvard School of Public Health. Study participants gave their written informed consent.
Exposure data were first treated as continuous variables, because logarithmic transformations reasonably approached a Gaussian distribution. Effects of contaminant exposures on outcome parameters were determined using standard regression techniques. Insulin concentrations and calculated insulin resistance and beta index were also log transformed to obtain normally distributed residuals with a homogeneous variance. Sex and BMI were considered obligatory covariates in the regression analyses. BMI at age 20 was considered more relevant to lifetime contaminant exposure and diabetes. The current BMI was included as an additional covariate in separate analyses along with lipid metabolism parameters (serum triglycerides, total cholesterol, and current use of lipid reducing medication). Age, current and past smoking (yes/no), and birth weight were also considered, however, none of these covariates was associated with the outcome at a P < 0.1 and were therefore disregarded. Exposure parameters were entered into the model, one at a time.
An odds ratio (OR) with the 95% confidence interval (CI) was calculated for the effect of a doubling of the contaminant exposure on the probability of having impaired fasting glycemia and type 2 diabetes (incident and known cases combined). We used multinomial logistic regression to assess the log odds for impaired fasting glycemia and diabetes relative to the normal status (referent group) for a unit change in the continuous predictor, or to the referent group for categorical variables.26,27 Associations with glucose metabolism variables were assessed by multiple regression analysis. Because of the logarithmic transformation of the PCB concentration, effects were expressed as the relative change of the outcome variables per doubling of the exposure, as calculated from the antilog of the regression coefficient, with the 95% CI. Residual plots were used to assess the model fit, and the possible significance of second- and third-order terms was determined.
As an additional exposure variable, we used the questionnaire information on traditional diet, ie, pilot whale meat and blubber, as well as seabirds, during childhood and adolescence, adulthood, and the past year. (Fish is not an important source of PCB and DDE in this population.) As 3 different dietary sources were considered, standard regression analysis with confounder adjustment was complemented by structural equation models to assess the association between the overall intake of traditional food at each of the 3 life stages. This approach has only recently been introduced in epidemiologic research, but detailed instructions are available.28,29 We considered the observed variables to be manifestations of a single latent variable (which cannot be observed but can be estimated from the variables recorded). Each of the dietary parameters depends linearly on the latent exposure variable; error terms for the 3 parameters are assumed to be independent, although local dependence can be modeled. The relationship between each latent diet variable and the outcomes was then considered after adjustment for the effects of covariates. In addition to avoiding multiple comparison problems, this method can adjust for exposure imprecision and missing data, which may not be adequately addressed by standard regression analyses.29
Descriptive analyses and regression models were carried out in SAS (version 9.1; SAS Institute Inc, Cary, NC) and R (version 2.10; http://www.R-project.org). SEMs were developed in Mplus (version 3.1; Muthen & Muthen, Los Angeles, CA).
One subject was excluded from the analyses due to the presence of alcoholic pancreatitis. Of the 712 remaining cohort members, a total of 168 septuagenarians (24% of the cohort) had type 2 diabetes, of whom 91 (13%) had been previously diagnosed with the disease; 77 incident cases (11%) were identified in the present study. Men were more likely to be diabetic (93 of 360, or 26%) than women (75 of 352, or 21%). Impaired fasting glycemia was found in 78 additional subjects (11%), of whom 36 were men and 42 women. The overall characteristics of the septuagenarians are shown in Table 1. Two subjects with birth weights of 1500 and 1700 g were considered outliers and were excluded from the calculations of the effects of birth weight (all other birth weights were ≥2500 g).
All subjects had eaten traditional food to some degree (notably pilot whale meat and blubber) and seabirds such as fulmar and puffin. The intake was particularly frequent in childhood and adolescence (from mid-1930s to early 1950s), somewhat lower in adulthood and substantially lower during the last year. Serum PCB concentrations covered a range from a background level of 0.7 μg/g lipid to a high level of 70 μg/g lipid (a 100-fold range). DDE averaged slightly less than half of the PCB concentration, and the 2 were highly correlated (r = 0.81 after log transformation). Both were associated with traditional food intake at various ages, whereas blood-mercury concentrations showed close correlation with recent whale meat intake (Table 2).
Of the risk factors considered, BMI was by far the most important predictor of type 2 diabetes and impaired glucose metabolism (Table 3). PCB correlated poorly with current BMI (r = −0.003) and more strongly with BMI at age 20 (r = 0.28). Mercury concentrations were associated with PCB and DDE, but not with diabetes or the risk factors.
After adjustment for sex and BMI at age 20, contaminant exposures and childhood/adolescence diet were associated with an increased risk of IFG and type 2 diabetes, although addition of further covariates somewhat weakened some of the associations (Table 4). While all of the odds ratios were >1, most estimates had fairly wide confidence intervals. The diet during adulthood showed less stable associations. No difference was apparent in these associations between men and women, and inclusion of an interaction parameter between BMI and PCB barely changed the results (data not shown).
Fasting plasma concentrations of insulin decreased at higher PCB levels in all nondiabetic subjects as well as in subjects with normal glucose tolerance (Table 5, Figure). The calculated beta index showed a similar association, but in diabetic subjects, fasting insulin concentrations did not show any clear trend (data not shown). Glucose concentrations increased at higher exposures. If further adjusted for the calculated insulin resistance, this positive association was strengthened (data not shown). On the other hand, glycosylated hemoglobin was not obviously related to the exposure. Associations with DDE and childhood/adolescence diet were consistent with the PCB results, although effect estimates were smaller and less stable (data not shown).
This cross-sectional study of a population-based sample of Faroese septuagenarians showed that type 2 diabetes and impaired fasting glycemia were associated with increased serum PCB concentrations and with a history of more frequent intake of traditional food in childhood and adolescence. In healthy subjects, increased PCB exposure was associated with a decreased fasting insulin concentration and increased fasting glucose. These findings support a possible effect of exposure to organochlorine substances on the pathogenesis of type 2 diabetes.
A major strength of this population-based study is the high participation rate among the elderly subjects within a narrow age range. The total prevalence of diabetes in the population sample was high (24%). US data suggest a prevalence of about 16% for subjects above 65 years, with fasting glucose suggesting an additional 6% having undiagnosed type 2 diabetes,30 although somewhat less if based on glycosylated hemoglobin.31 Among the Faroese septuagenarians, slightly more than half had been previously diagnosed with type 2 diabetes, and the clinical examination therefore discovered a considerable number of new cases. In addition, 11% had impaired fasting glycemia.
The serum PCB concentrations are highly elevated in this population. The main source is pilot whale blubber; with an average PCB concentration of about 20 μg/g,32 an estimated average intake of 50 g per week would result in a weekly PCB intake of 1 mg. A PCB exposure of similar magnitude was calculated for highly-exposed Great Lakes anglers at an average annual level of 46.5 mg.33 Because of the long elimination half-life of major PCB congeners, the serum PCB concentration represents a long-term accumulation, although the serum concentration and the total body burden depend on the size of the lipid compartment. Further, the capability of PCB elimination is greater in slim subjects.18 Thus, the impacts of BMI on serum PCB concentrations and the greater diabetes risk in obese subjects may cloud any diabetogenic effect reflected by the current serum PCB concentration.
Stronger evidence of an increased diabetes risk appears from the decreasing fasting insulin concentrations at higher PCB concentrations in subjects without diabetes or without impaired fasting glycemia. The concomitant increase in fasting glucose supported this tendency. These observations are in accordance with possible beta cell toxicity or exhaustion, a mechanism supported by experimental toxicity studies, although the release of insulin increases in the short term.2 Decreased fasting plasma-insulin in highly exposed subjects has been reported previously,14,15 although a positive association with increased dioxin exposures has been observed in younger adults.9,12
The apparently discrepant findings should be considered in the light of different stages of the pathogenesis of type 2 diabetes mellitus. The development of this illness is thought to initially include a phase of increasing insulin resistance, compensated by an increase in insulin secretion to maintain normal plasma glucose concentrations. With time, beta cells become exhausted as a result of the insulin resistance, perhaps coupled with the impact of toxic influences.34 Thus, our results suggest that organochlorine exposure may be associated with both insulin insensitivity and beta cell toxicity, in agreement with experimental studies.2 Several mechanisms of beta cell toxicity may be involved, including activation by dioxin-related substances of the intranuclear aryl hydrocarbon receptor.35
Previous observations of dioxin-associated increases in fasting plasma insulin concentrations in younger subjects would fit with a pattern of initial stimulation of insulin secretion, perhaps triggered by early insulin insensitivity. The increased fasting insulin concentration in exposed adults may later (as observed in the septuagenarians examined in the present study) be reversed as a sign of beta cell depletion. This change could be a further step in the development of type 2 diabetes mellitus, especially if it coincides with obesity. All of the underlying epidemiologic data originate from cross-sectional studies and not from populations prospectively followed through decades. Thus, further research is needed to elucidate the role of organochlorine pollutants in human diabetes pathogenesis.
The possible role of individual or groups of PCB congeners in diabetes etiology cannot be ascertained from this study due to the mixed exposure and the high correlation among their serum concentrations. Although some PCB congeners have dioxin-like toxicity properties, the overall dioxin exposure in the Faroe Islands appears not to be increased above the northern European average.36 The DDE concentrations are also elevated, however, exposures to chlorinated pesticides other than DDE are comparatively low. In a US population-based study, serum concentrations of 6 pollutants detectable in at least 80% of the participants showed an adjusted odds ratio of 38 for diabetes in subjects in the highest exposure quintile, as compared with those in the lowest.8 All pollutants seemed to contribute to the increased risk, but all of them are also highly persistent. Current serum measures serve as markers of past and cumulated exposures to environmental chemicals, some of which may have been eliminated over time. Among possible candidates as diabetogenic substances are the brominated flame retardants,37 but exposures to many of these persistent pollutants are interrelated. Increased consumption of oily fish, which may contain lipophilic contaminants, seems not to reduce the risk of diabetes, and high intakes may increase the incidence of this disease,38 further suggesting a possible role of lipophilic seafood contaminants. At this point, the identity and specific effects of the potentially causative substance(s) remains unclear. The relatively small odds ratios observed in the highly exposed Faroese subjects indicate that a possible diabetes risk may not increase linearly with the dose. However, the odds ratios may have been affected by the small number of subjects with low exposure.
An important weakness is that the single measurement of PCBs at age 70–74 years is likely to be an imprecise indicator of the life-time exposure to the causative contaminants, in part because changes in BMI may affect serum PCB concentrations. Such imprecision would tend to cause a bias toward the null and underestimate the effect. The same applies to the use of questionnaire answers on past diets, which is exacerbated by the absence of information on past concentrations of contaminants in traditional food. The discovery of PCBs and other persistent organic pollutants in the environment dates back to the 1970s, but sediment analyses suggest that substantial amounts were already passing into global food chains during the 1950s.39,40 The septuagenarians examined in this study were therefore exposed to these substances since childhood.
The increasing worldwide prevalence of type 2 diabetes is in part a result of an increased survival of the diabetic population due to improved treatment, but it is also a result of unhealthy, sedentary lifestyle, and an energy-dense diet, both resulting in an increased body weight.1 If environmental pollutants play a role in triggering type 2 diabetes, prevention may need to involve mechanisms other than individual intervention, as these substances are generally invisible to the consumer and may be difficult to address within current health-care systems. The contaminants studied so far have now largely been banned, and exposures to these contaminants have recently decreased. However, those now approaching the age with the greatest diabetes incidence were born at a time when environmental accumulation of these pollutants was at a peak, and the developmental programming of glucose metabolism may therefore have been affected by diabetogenic chemicals.16 Intensified prevention of exposure to environmental pollutants should be considered as an attractive means of complementing preventive efforts against type 2 diabetes.
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